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	<title>Ministry of Water DCOM Manual - User contributions [en]</title>
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	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=533</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=533"/>
		<updated>2020-03-31T14:03:25Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Preface|Preface]] || i&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Acknowledgements|Acknowledgements]] || ii&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[List_of_Special_Committee_Members|List of Special Committee Members]] || iii&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[List_of_Abbreviations|List of Abbreviations]] || iv&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 15 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 16 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 17 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 18 || Apendices: Appendices&lt;br /&gt;
* [[DCOM Volume I Appendix A|Appendix A: Climate Change and Resilience to Climate Change	]]&lt;br /&gt;
* [[DCOM Volume I Appendix B|Appendix B: Minimum Water Flow Requirement for Fire Fighting	]]&lt;br /&gt;
* [[DCOM Volume I Appendix C|Appendix C: Example: Estimating The Capacity Of Tank	]]&lt;br /&gt;
* [[DCOM Volume I Appendix D|Appendix D: Structural Design of Concrete	]]&lt;br /&gt;
* [[DCOM Volume I Appendix E|Appendix E: Supply Pumping Systems	]]&lt;br /&gt;
* [[DCOM Volume I Appendix F|Appendix F: Source of Pumping Power	]]&lt;br /&gt;
* [[DCOM Volume I Appendix G|Appendix G: Additional Details of Various Unit Oprations	]]&lt;br /&gt;
* [[DCOM Volume I Appendix H|Appendix H: Methods for Disinfecting Water	]]&lt;br /&gt;
* [[DCOM Volume I Appendix I|Appendix I: Measurements of Water Hardness	]]&lt;br /&gt;
* [[DCOM Volume I Appendix J|Appendix J: Basic Statistics Used in Estimation of Design of Flood Events	]]&lt;br /&gt;
* [[DCOM Volume I Appendix K|Appendix K: Dams Detail Design	]]&lt;br /&gt;
* [[DCOM Volume I Appendix L|Appendix L: Standard Drawings	]]&lt;br /&gt;
* [[DCOM Volume I Appendix M|Appendix M: Selected Intake Designs	]]&lt;br /&gt;
* [[DCOM Specification|Appendix O: Standard Specifications	]]&lt;br /&gt;
|| 231&lt;br /&gt;
|}&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I_Appendix_L&amp;diff=532</id>
		<title>DCOM Volume I Appendix L</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I_Appendix_L&amp;diff=532"/>
		<updated>2020-03-31T13:37:33Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;=Appendix L: Standard Drawings =&lt;br /&gt;
This is a list of standard drawings of common structures associated with drinking supply structure; it enables engineers and project managers to save time during design, and preparation of design report and most importantly during implementation by using drawing and bill of quantity  from the Tanzania Ministry of Water  [https://www.maji.go.tz Website], then clic on the [http://design.maji.go.tz/index.php/Main_Page Design Manual (DCOM)] link under the e-Service section. &lt;br /&gt;
&lt;br /&gt;
{| class=&amp;quot;wikitable sortable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! S/No !! Drawing Name !! Drawing Number !! PDF File!! AutoCAD File&lt;br /&gt;
|-&lt;br /&gt;
| 1 || Intake of clear stream-to be found on rock/soft ground || TY/ST/40 || [[:File:TS-YT-40-2020-03-07.pdf| TY-ST-40]]|| [[:File:TY-ST-40-AutoCAD.dwg| TY-ST-40 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 2 || Typical sand trap intake (small stream) || 22109 || [[:File:22109.pdf| 22109 PDF]] || [[:File:22109.dwg| 22109 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 3 || Spring intake structure (spring box) || MAR/SK/150 || [[:File:MARK-SK-150.pdf| MARK-SK-150 PDF]] ‎|| [[:File:MARK-SK-150-AutoCAD.dwg| MARK-SK-150 AutoCAD]] &lt;br /&gt;
|-&lt;br /&gt;
| 4 || Single and double tap domestic point (Type IA &amp;amp; IB) || TY/WS/23 || [[:File:Domestic_Point.pdf| TY-WS-23  PDF]] || [[:File:Domestic_Point.dwg| TY-WS-23 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 5 || Substitute to domestic point type (Box Kiosk design type A) || S/MO/1051 ||  [[:File:Box_kiosk_design.pdf| S-MO-1051  PDF]] || [[:File:Box_kiosk_design.dwg| S-MO-1051 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 6 || Type borehole pump house (with Lister 6 H.P engine &amp;amp;  Climax 28/3 well head) || TY/ST/12/A || [[:File:Borehole_Pump_House.pdf| TY-ST-12-A PDF]]|| [[:File:Borehole_Pump_House.dwg| TY-ST-12-A AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 7 || Type pump house for centrifugal pump || TY/ST/49|| [[:File:TY-ST-49.pdf| TY-ST-49 PDF]]|| [[:File:TY-ST-49.dwg| TY-ST-49 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 8 || Break pressure tank combined with Domestic point and washing slab || S/MO/852 || [[:File:Break_Pressure_Tank.pdf| S-MO-852 PDF]]|| [[:File:Break_Pressure_Tank.dwg| S-MO-852 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 9 || Short cattle trough || TY/TA/5 || [[:File:TY-TA-5.pdf| TY-TA-5 PDF]]|| [[:File:TY-TA-5.dwg| TY-TA-5 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 10 || Short Goat and sheep trough || S/MO/880 || [[:File:S-MO-880.pdf| S-MO-880 PDF]]|| [[:File:S-MO-880.dwg| S-MO-880 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 11 || Spring weir || MAR/SK/146 || [[:File:MAR-SK-146.pdf| MAR-SK-146 PDF]]|| [[:File:MAR-SK-146.dwg| MAR-SK-146 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 12 || Slow sand filter capacity 22.5m3 per day || TY/TA/54 || [[:File:Sand_Filter.pdf| TY-TA-54 PDF]]|| [[:File:Sand_Filter.dwg| TY-TA-54 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 13 || 45m 3 CIRCULAR TANK WITH REINFORCED  COVER || S/AR/370 || [[:File:45m3_Ground_Tank.pdf| S-AR-370  PDF]]|| [[:File:45m3_Ground_Tank.dwg|S-AR-370  AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 14 || 45m3 R.C CIRCULAR TANK ON 6m HIGH CONCRETE BLOCKWORK RISER || S/MO/826 || [[:File:45m3_Tank_on_6m_Riser.pdf| S-MO-826  PDF]]|| [[:File:45m3_Tank_on_6m_Riser.dwg|S-MO-826  AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 15 || 90m3 R.C CIRCULAR TANK GROUND TANK || S/MO/257 ||[[:File:90m3_Ground_Tank.pdf| S-MO-257  PDF]]|| [[:File:90m3_Ground_Tank.dwg|S-MO-257  AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 16 || 90m3 R.C CIRCULAR TANK ON 6m HIGH CONCRETE BLOCKWORK RISER || S/MO/827 ||[[:File:90m3_Tank_on_6m_Riser.pdf| S-MO-827 PDF]]|| [[:File:90m3_Tank_on_6m_Riser.dwg|S-MO-827  AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 17 || 135m3 CIRCULAR TANK WITH REINFORCED  COVER || TY/TA/14 || [[:File:135m3_Ground_Tank.pdf| TY-TA-14 PDF]]|| [[:File:135m3_Ground_Tank.dwg| TY-TA-14 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 18 || 135m 3 R.C CIRCULAR TANK ON 6m HIGH CONCRETE BLOCKWORK RISER || TY/TA/41/A || [[:File:135m3_Tank_on_6m_Riser.pdf| TY-TA-14-A PDF]] || [[:File:135m3_Tank_on_6m_Riser.dwg| TY-TA-14-A AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 19 || 225m3 R.C CIRCULAR TANK ON GROUND || S/MO/843 || [[:File:225m3_Ground_Tank.pdf| S-MO-843 PDF]] || [[:File:225m3_Ground_Tank..dwg| S-MO-843 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 20 || 225m3 R.C CIRCULAR TANK ON 6m HIGH CONCRETE BLOCKWORK RISER || 12230 || [[:File:225m3_Tank_on_6m_Riser.pdf| 12230 PDF]] || [[:File:225m3_Tank_on_6m_Riser.dwg| 12230 AutoCAD]]&lt;br /&gt;
|}&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I_Appendix_L&amp;diff=531</id>
		<title>DCOM Volume I Appendix L</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I_Appendix_L&amp;diff=531"/>
		<updated>2020-03-31T13:36:23Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: Created page with &amp;quot;This is a list of standard drawings of common structures associated with drinking supply structure; it enables engineers and project managers to save time during design, and p...&amp;quot;&lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;This is a list of standard drawings of common structures associated with drinking supply structure; it enables engineers and project managers to save time during design, and preparation of design report and most importantly during implementation by using drawing and bill of quantity  from the Tanzania Ministry of Water  [https://www.maji.go.tz Website], then clic on the [http://design.maji.go.tz/index.php/Main_Page Design Manual (DCOM)] link under the e-Service section. &lt;br /&gt;
&lt;br /&gt;
{| class=&amp;quot;wikitable sortable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! S/No !! Drawing Name !! Drawing Number !! PDF File!! AutoCAD File&lt;br /&gt;
|-&lt;br /&gt;
| 1 || Intake of clear stream-to be found on rock/soft ground || TY/ST/40 || [[:File:TS-YT-40-2020-03-07.pdf| TY-ST-40]]|| [[:File:TY-ST-40-AutoCAD.dwg| TY-ST-40 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 2 || Typical sand trap intake (small stream) || 22109 || [[:File:22109.pdf| 22109 PDF]] || [[:File:22109.dwg| 22109 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 3 || Spring intake structure (spring box) || MAR/SK/150 || [[:File:MARK-SK-150.pdf| MARK-SK-150 PDF]] ‎|| [[:File:MARK-SK-150-AutoCAD.dwg| MARK-SK-150 AutoCAD]] &lt;br /&gt;
|-&lt;br /&gt;
| 4 || Single and double tap domestic point (Type IA &amp;amp; IB) || TY/WS/23 || [[:File:Domestic_Point.pdf| TY-WS-23  PDF]] || [[:File:Domestic_Point.dwg| TY-WS-23 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 5 || Substitute to domestic point type (Box Kiosk design type A) || S/MO/1051 ||  [[:File:Box_kiosk_design.pdf| S-MO-1051  PDF]] || [[:File:Box_kiosk_design.dwg| S-MO-1051 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 6 || Type borehole pump house (with Lister 6 H.P engine &amp;amp;  Climax 28/3 well head) || TY/ST/12/A || [[:File:Borehole_Pump_House.pdf| TY-ST-12-A PDF]]|| [[:File:Borehole_Pump_House.dwg| TY-ST-12-A AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 7 || Type pump house for centrifugal pump || TY/ST/49|| [[:File:TY-ST-49.pdf| TY-ST-49 PDF]]|| [[:File:TY-ST-49.dwg| TY-ST-49 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 8 || Break pressure tank combined with Domestic point and washing slab || S/MO/852 || [[:File:Break_Pressure_Tank.pdf| S-MO-852 PDF]]|| [[:File:Break_Pressure_Tank.dwg| S-MO-852 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 9 || Short cattle trough || TY/TA/5 || [[:File:TY-TA-5.pdf| TY-TA-5 PDF]]|| [[:File:TY-TA-5.dwg| TY-TA-5 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 10 || Short Goat and sheep trough || S/MO/880 || [[:File:S-MO-880.pdf| S-MO-880 PDF]]|| [[:File:S-MO-880.dwg| S-MO-880 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 11 || Spring weir || MAR/SK/146 || [[:File:MAR-SK-146.pdf| MAR-SK-146 PDF]]|| [[:File:MAR-SK-146.dwg| MAR-SK-146 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 12 || Slow sand filter capacity 22.5m3 per day || TY/TA/54 || [[:File:Sand_Filter.pdf| TY-TA-54 PDF]]|| [[:File:Sand_Filter.dwg| TY-TA-54 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 13 || 45m 3 CIRCULAR TANK WITH REINFORCED  COVER || S/AR/370 || [[:File:45m3_Ground_Tank.pdf| S-AR-370  PDF]]|| [[:File:45m3_Ground_Tank.dwg|S-AR-370  AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 14 || 45m3 R.C CIRCULAR TANK ON 6m HIGH CONCRETE BLOCKWORK RISER || S/MO/826 || [[:File:45m3_Tank_on_6m_Riser.pdf| S-MO-826  PDF]]|| [[:File:45m3_Tank_on_6m_Riser.dwg|S-MO-826  AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 15 || 90m3 R.C CIRCULAR TANK GROUND TANK || S/MO/257 ||[[:File:90m3_Ground_Tank.pdf| S-MO-257  PDF]]|| [[:File:90m3_Ground_Tank.dwg|S-MO-257  AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 16 || 90m3 R.C CIRCULAR TANK ON 6m HIGH CONCRETE BLOCKWORK RISER || S/MO/827 ||[[:File:90m3_Tank_on_6m_Riser.pdf| S-MO-827 PDF]]|| [[:File:90m3_Tank_on_6m_Riser.dwg|S-MO-827  AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 17 || 135m3 CIRCULAR TANK WITH REINFORCED  COVER || TY/TA/14 || [[:File:135m3_Ground_Tank.pdf| TY-TA-14 PDF]]|| [[:File:135m3_Ground_Tank.dwg| TY-TA-14 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 18 || 135m 3 R.C CIRCULAR TANK ON 6m HIGH CONCRETE BLOCKWORK RISER || TY/TA/41/A || [[:File:135m3_Tank_on_6m_Riser.pdf| TY-TA-14-A PDF]] || [[:File:135m3_Tank_on_6m_Riser.dwg| TY-TA-14-A AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 19 || 225m3 R.C CIRCULAR TANK ON GROUND || S/MO/843 || [[:File:225m3_Ground_Tank.pdf| S-MO-843 PDF]] || [[:File:225m3_Ground_Tank..dwg| S-MO-843 AutoCAD]]&lt;br /&gt;
|-&lt;br /&gt;
| 20 || 225m3 R.C CIRCULAR TANK ON 6m HIGH CONCRETE BLOCKWORK RISER || 12230 || [[:File:225m3_Tank_on_6m_Riser.pdf| 12230 PDF]] || [[:File:225m3_Tank_on_6m_Riser.dwg| 12230 AutoCAD]]&lt;br /&gt;
|}&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
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		<updated>2020-03-31T12:26:51Z</updated>

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*DCOM Volumes&lt;br /&gt;
** DCOM_Volume_I|Volume I&lt;br /&gt;
** Volume_II:_Preface|Volume II&lt;br /&gt;
** Volume_III:_Preface|Volume III&lt;br /&gt;
** Volume_IV:_Preface|Volume IV&lt;br /&gt;
*DCOM Specifications&lt;br /&gt;
** Appendix_N:_Specifications|General Specifications&lt;br /&gt;
** Appendix_N:_Specifications|Standard Specifications&lt;br /&gt;
*DCOM Drawings&lt;br /&gt;
** Appendix_M:_Standard_Drawings|Engineering Drawings&lt;br /&gt;
* SEARCH&lt;br /&gt;
* TOOLBOX&lt;br /&gt;
* LANGUAGES&lt;/div&gt;</summary>
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&lt;div&gt;&lt;br /&gt;
* navigation&lt;br /&gt;
** mainpage|mainpage-description&lt;br /&gt;
*DCOM Volumes&lt;br /&gt;
** DCOM_Volume_I|DCOM Volume I&lt;br /&gt;
** Volume_II:_Preface|DCOM Volume II&lt;br /&gt;
** Volume_III:_Preface|DCOM Volume III&lt;br /&gt;
** Volume_IV:_Preface|DCOM Volume IV&lt;br /&gt;
** Appendix_N:_Specifications|DCOM Specifications&lt;br /&gt;
** Appendix_M:_Standard_Drawings|DCOM Drawings&lt;br /&gt;
** recentchanges-url|recentchanges&lt;br /&gt;
* SEARCH&lt;br /&gt;
* TOOLBOX&lt;br /&gt;
* LANGUAGES&lt;/div&gt;</summary>
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** DCOM_Volume_I|DCOM Volume I&lt;br /&gt;
** Volume_II:_Preface|DCOM Volume II&lt;br /&gt;
** Volume_III:_Preface|DCOM Volume III&lt;br /&gt;
** Volume_IV:_Preface|DCOM Volume IV&lt;br /&gt;
** Appendix_N:_Specifications|DCOM Specifications&lt;br /&gt;
** Appendix_M:_Standard_Drawings|DCOM Drawings&lt;br /&gt;
** recentchanges-url|recentchanges&lt;br /&gt;
* SEARCH&lt;br /&gt;
* TOOLBOX&lt;br /&gt;
* LANGUAGES&lt;/div&gt;</summary>
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** DCOM_Volume_I|DCOM Volume I&lt;br /&gt;
** Volume_II:_Preface|DCOM Volume II&lt;br /&gt;
** Volume_III:_Preface|DCOM Volume III&lt;br /&gt;
** Volume_IV:_Preface|DCOM Volume IV&lt;br /&gt;
** Appendix_N:_Specifications|DCOM General Specifications&lt;br /&gt;
** Appendix_M:_Standard_Drawings|DCOM Standard Drawings&lt;br /&gt;
** recentchanges-url|recentchanges&lt;br /&gt;
* SEARCH&lt;br /&gt;
* TOOLBOX&lt;br /&gt;
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		<title>Chapter Two: Project Planning</title>
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&lt;div&gt;Arguably, planning of water supply projects is considered to be one of the most important stages in the design. Thus, it is strongly advised and emphasized that much time should be spent to undertake proper project planning. A proper project planning will ensure effective and efficient completion of the project successfully. In this chapter, project planning is presented in seven parts that are detailed below. These include:&lt;br /&gt;
&lt;br /&gt;
* Planning considerations for water supply projects&lt;br /&gt;
* Project Planning steps&lt;br /&gt;
* Consulting the Integrated Water Resources Management and Development Plan&lt;br /&gt;
* Consult guideline for preparation of Water Safety Plan – resilient to climate change.&lt;br /&gt;
* Environmental and Social Impact Assessment (ESIA) and Strategic Environmental and Social Impact Assessment (SESIA) Compliance&lt;br /&gt;
* Potential Impacts of Climate Change on Water Supply Projects&lt;br /&gt;
* Participation of CBWSOs in Project Planning Stages&lt;br /&gt;
&lt;br /&gt;
&amp;lt;div class=&amp;quot;noautonum&amp;quot;&amp;gt;__TOC__&amp;lt;/div&amp;gt;&lt;br /&gt;
&lt;br /&gt;
=Chapter Two: Project Planning=&lt;br /&gt;
&lt;br /&gt;
==2.1	Planning Considerations for Water Supply Projects ==&lt;br /&gt;
Before commencement of any development of a water project, it is essential to conduct project planning. Planning is a process that should entail the following:&lt;br /&gt;
•	Undertake ESIA and SESIA studies,&lt;br /&gt;
•	Engagement and involvement of the local community to instill the ownership, provide the local knowledge, project buy in and accommodate community needs and requirements,&lt;br /&gt;
•	Assess safe and reliable yield or discharge and quality of water source,&lt;br /&gt;
•	Determination of the system layout,&lt;br /&gt;
•	Conduct design of the water supply project,&lt;br /&gt;
•	Implement the project in terms of construction, operation and maintenance,&lt;br /&gt;
•	Work out to obtain a sound and robust project financing.&lt;br /&gt;
&lt;br /&gt;
It should be emphasized and stressed that collection of good quality, reliable, credible and enough data should be given high priority at all stages of project implementation. Population projection methods and their relevance for rural and urban settings or areas as recommended by the National Bureau of Statistics (NBS) have to be evaluated. Demographic features such as social and economic conditions have to be studied before design projections can be established. Also, water source reliability should be carried out before any further stage of project implementation.&lt;br /&gt;
==2.2	Project Planning Steps==&lt;br /&gt;
Project planning involves a series of steps that determine how project goals will be achieved. The goals may be solicited from the existing community or a strategic plan. In an event that there is not any plan, project plans can be developed through community meetings and gatherings, councils or board meetings, special focused group discussions or other planning processes. &lt;br /&gt;
&lt;br /&gt;
The main steps of project planning include:&lt;br /&gt;
* Step 1: Initiation&lt;br /&gt;
* Step 2: Pre-feasibility study&lt;br /&gt;
* Step 3: Feasibility study&lt;br /&gt;
* Step 4: Preliminary and Detailed Design&lt;br /&gt;
* Step 5: Project phasing&lt;br /&gt;
* Step 6: Procurement&lt;br /&gt;
* Step 7: Implementation/Construction&lt;br /&gt;
* Step 8: Operation and Maintenance (Management)&lt;br /&gt;
* Step 9: Performance Monitoring&lt;br /&gt;
&lt;br /&gt;
The planning of water supply projects can be represented diagrammatically by a step wise planning cycle as shown in Figure 2.1.&lt;br /&gt;
&lt;br /&gt;
==2.3	Pump Protection==&lt;br /&gt;
The following sections provide a brief description of each of the twelve project planning steps.&lt;br /&gt;
&lt;br /&gt;
===2.3.1	Initiation===&lt;br /&gt;
Initiation or sometimes referred to as triggering stage, is a step where initial ideas of the project are presented. Community mobilization through awareness raising is conducted at this stage. The whole idea is to inform the community on the start of the project, solicit community input and knowledge about the project area. Project common understanding is also expected to be realized at this step. &lt;br /&gt;
&lt;br /&gt;
The outcome of this stage of planning is to acquire an understanding of the community conditions and identify problems that prevent the community from achieving its long-range goals. Community conditions which must be collected includes aspects of the community such as: &lt;br /&gt;
* Its geographic location, &lt;br /&gt;
* Demographics, &lt;br /&gt;
* Ecosystem, &lt;br /&gt;
* History,e.t.c&lt;br /&gt;
&lt;br /&gt;
The data collection for the above information should employ community assessment methods.&lt;br /&gt;
&lt;br /&gt;
[[File:Volume I Figure 2.1 Projects Planning Process.png|thumb|Figure 2.1: Projects Planning Process]]&lt;br /&gt;
&lt;br /&gt;
(Source: Modified after Design Manual 3rd edition, 2009)&lt;br /&gt;
 &lt;br /&gt;
====2.3.1.1	Community Assessment Steps====&lt;br /&gt;
* Identify specific community problems that stand in the way of meeting community goals. Produce a community problem statement,&lt;br /&gt;
* Creates a work plan for addressing problems and attaining the goals, &lt;br /&gt;
* Describe measurable beneficial impacts to the community that result from the project’s implementation, &lt;br /&gt;
* Determine the level of resources or funding necessary to implement the project.&lt;br /&gt;
* Solicit community social economic assessment report from Local Government Authorities for use in choice of technology to achieve project sustainability&lt;br /&gt;
&lt;br /&gt;
====2.3.1.2	 Methods of conducting community assessment====&lt;br /&gt;
Two methods can be employed for conducting community assessment. They are comprehensive and strategic planning.&lt;br /&gt;
&lt;br /&gt;
=====2.3.1.2.1	Comprehensive community assessment=====&lt;br /&gt;
This process should involve:&lt;br /&gt;
* Completing a community-wide needs assessment to engage the community in identifying and prioritizing all long-range goals and the community problems preventing the achievement of those goals, &lt;br /&gt;
* Next, the community is involved in the process of developing a method to accomplish long-range goals,  &lt;br /&gt;
* Discussing initial ways to overcome the problems &lt;br /&gt;
* Develop measures to monitor progress towards achieving those goals. &lt;br /&gt;
&lt;br /&gt;
Comprehensive plans require at least a year to complete and should cover a five- to ten-year time span. &lt;br /&gt;
&lt;br /&gt;
======2.3.1.2.2	Strategic community assessment======&lt;br /&gt;
This is a process used when a community or an organization already has a comprehensive plan and wants to move forward to achieve its long-range goals. Strategic planning involves:&lt;br /&gt;
Participation of the community in identifying problems that stand between the community and its goals and to move the community towards realizing its long-range vision. &lt;br /&gt;
&lt;br /&gt;
The product of strategic planning, simply called the “strategic plan,” builds on pre-established long-range goals by designing projects related to one or more of these goals. A strategic plan generally takes at least six months to complete.&lt;br /&gt;
&lt;br /&gt;
===2.3.2	Pre-feasibility Study===&lt;br /&gt;
The pre-feasibility study stage involves initial fieldwork and studies of alternative water resource development plans. The report issued is an outline of possibilities and a list of all the fieldwork activities that need to be accomplished at a feasibility study or even a preliminary engineering design stage.&lt;br /&gt;
&lt;br /&gt;
The objective of this initial study is to determine whether it is worthwhile to proceed with more detailed investigations. In other words at this stage, various projects or alternatives are screened and this should normally reduce the number of options considered feasible to no more than three or so. The report should, however, contain recommendations on the proposed project and how to proceed with the detailed investigations.&lt;br /&gt;
&lt;br /&gt;
These should include indications on the following:&lt;br /&gt;
&lt;br /&gt;
* Data to be collected,&lt;br /&gt;
* Remaining alternatives to be considered and investigated,&lt;br /&gt;
* Professional human resources required,&lt;br /&gt;
* Estimate of time that will be taken or needed,&lt;br /&gt;
* Budgetary financial requirements.&lt;br /&gt;
&lt;br /&gt;
The above are considered taking into account:&lt;br /&gt;
&lt;br /&gt;
* Long term needs,&lt;br /&gt;
* Deficiencies in the existing system (if any),&lt;br /&gt;
* Phases of project implementation.&lt;br /&gt;
&lt;br /&gt;
Briefly, the pre-feasibility report should give an outline of the future development, which seems most appropriate to provide the project area with water in the long term. The other major aim may be to select a short-term project that may be implemented to overcome any immediate needs (crash programme) while the long-term project is being prepared. &lt;br /&gt;
&lt;br /&gt;
===2.3.3	Feasibility Study===&lt;br /&gt;
The feasibility study stage develops the pre-feasibility work further and ends with a Report which normally concentrates on the project alternatives that were recommended for more detailed consideration at the pre-feasibility stage.&lt;br /&gt;
&lt;br /&gt;
The study has to be carried out by a team of competent and experienced personnel from the Ministry, RUWASA and WWSA or with the help of a private sector. At this stage, the following should be achieved:&lt;br /&gt;
&lt;br /&gt;
* Collection of sufficient design data,&lt;br /&gt;
* Appraise the alternatives,&lt;br /&gt;
* Alternative plans (projects) adequately studied and evaluated,&lt;br /&gt;
* Socio-economic analysis adequately conducted and completed&lt;br /&gt;
* Solicit the views and preferences with community in an open meeting&lt;br /&gt;
* Discuss the merits and demerits with community representatives&lt;br /&gt;
* Rank alternatives on the basis of appropriate costing method and perceived ability of community to afford the costs of operation and maintenance and reach agreement in principle with concerned water officials.&lt;br /&gt;
* Inform the community reasons for selection of the alternative(s) and seek their agreement and approval.&lt;br /&gt;
* Conduct Environmental Impact assessment (EIA). For larger projects a statement on Life Cycle Assessment should be included indicating the extent of quantitative and other relevant information currently available,&lt;br /&gt;
* Preliminary engineering design done, including a review of alternative materials,&lt;br /&gt;
* Preliminary cost estimates done,&lt;br /&gt;
* Economic internal rate of return and financial internal rate of return,&lt;br /&gt;
* Carry out design to a level sufficient to enable construction to proceed either using local (District) based contractors or a Force Account approach using local sub-contractors as considered feasible and appropriate,&lt;br /&gt;
* Most feasible project (least cost) selected, &lt;br /&gt;
* Feasibility report prepared and presented to the authorities for approval&lt;br /&gt;
&lt;br /&gt;
The report may also include interim progress reports, appendices of data collected during the detailed study. The feasibility report should be presented as a supporting document to apply for financing from the financing agencies.&lt;br /&gt;
====2.3.3.1	 Water Supply Projects Ranking and Technology Selection Criteria====&lt;br /&gt;
=====2.3.3.1.1	Ranking of Projects=====&lt;br /&gt;
Projects to be implemented should be ranked on the basis of the following criteria;&lt;br /&gt;
* Type of technology,&lt;br /&gt;
* Quantity of water,&lt;br /&gt;
* ESIA Report comments,&lt;br /&gt;
* Negative environment impact,&lt;br /&gt;
* Quality of water available,&lt;br /&gt;
* Cost/benefit analysis, &lt;br /&gt;
* Walking distance scheme complexity.&lt;br /&gt;
&lt;br /&gt;
=====2.3.3.1.2	Choice of Technology=====&lt;br /&gt;
As far as possible ranking of project selection is concerned, technology choice should be based on progressive consideration of:&lt;br /&gt;
* Hand pump(s) from proven permanent deep hand dug well(s) or shallow borehole(s),&lt;br /&gt;
* Gravity scheme from protected spring,&lt;br /&gt;
* Medium or deep well with appropriate hand pump (rotary type),&lt;br /&gt;
* Pumped / Piped Scheme Electrical Driven,&lt;br /&gt;
* Pumped/Piped Scheme Solar Driven.&lt;br /&gt;
&lt;br /&gt;
For point water sources or simple distribution systems, a prime location for a domestic point should be the village primary school followed by a village health facility (if any). Provision of improved sanitation and hand washing facilities at both primary school and health facility should also receive priority consideration in any village scheme. Use the relevant WASH guidelines for design of the washing facilities.&lt;br /&gt;
&lt;br /&gt;
===2.3.4	Preliminary and Detailed Design===&lt;br /&gt;
After the feasibility report is presented and approved, the preliminary and the preferred alternative should be selected and the finances sought. The following should be considered while conducting the design:&lt;br /&gt;
* The Engineer should prepare the preliminary engineering design and then the detailed or final project report,  &lt;br /&gt;
* These reports should provide the basis for implementation,  &lt;br /&gt;
* The initial report has to provide the design basics which are then developed further in the detailed design of the project including working drawings and tender documents,  &lt;br /&gt;
* They should however include a review of all relevant aspects of this DCOM Manual and either accept or otherwise indicate, complete with detailed reasoning, why different criteria is proposed. &lt;br /&gt;
&lt;br /&gt;
In addition, the report should address the following:&lt;br /&gt;
* The issue of costing being adopted and requirement for extent of whole life cycle analysis and adaptation of costing,  &lt;br /&gt;
* Consideration of the environmental impacts of the project and its envisaged elements,  &lt;br /&gt;
* Issue of climate change and its possible effects on the project being designed. &lt;br /&gt;
&lt;br /&gt;
It should be noted that the conceptual designs provided at the feasibility study or preliminary engineering stages are generally inadequate for the construction of the project. Foremost, the Engineer arranges for any outstanding detailed field investigations, surveys and data collection. Based on the detailed field data collected; detailed designs, plans and estimates are prepared.&lt;br /&gt;
&lt;br /&gt;
Detailed designs should include:&lt;br /&gt;
* Statistical analysis of data collected for the population and demand projections; hydrological ,hydrogeological  and meteorological data,&lt;br /&gt;
* Least cost lay-outs for different components of the project, i.e. treatment plants, hydraulic and structural works,&lt;br /&gt;
* Structural and stability computations of different structures,&lt;br /&gt;
* Calculations for pumps, motors, power generators and other machinery and equipment,&lt;br /&gt;
* Engineering analysis for deciding the most economic size of delivery mains.&lt;br /&gt;
* Hydraulic computations for the distribution system,&lt;br /&gt;
* Bills of quantities.&lt;br /&gt;
* Detailed design should include the following:&lt;br /&gt;
&lt;br /&gt;
====2.3.4.1	Detailed Engineering Drawings====&lt;br /&gt;
These should include:&lt;br /&gt;
&lt;br /&gt;
* Index plan showing overall layout of the project,&lt;br /&gt;
* Schematic diagram showing levels of salient components of the project (may not necessarily be to scale),&lt;br /&gt;
* Detailed plans and sections in scale for the headwords, treatment plants, clear water storage tank, pumping station, in a scale 1:20 to 1:100 depending on the details and size of the works,&lt;br /&gt;
* Detailed structural plans for structures, intake, treatment plant, clear water reservoir etc., in a scale of 1:20,&lt;br /&gt;
* Index plan of the distribution system normally in an appropriate scale,&lt;br /&gt;
* Longitudinal sections of the delivery main and details of appurtenances in scales: Horizontal scale 1:500 to 1:5000 depending on distance and details Vertical scale 1:20 to 1:100 depending on the terrain surface undulations.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.2		Detailed estimates of capital costs====&lt;br /&gt;
Project cost estimates should be based on unit costs derived from recent projects of a similar magnitude, complexity and remoteness from or proximity to ports or major urban areas.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.3	 Detailed estimates of recurrent costs====&lt;br /&gt;
As far as possible this should be based on unit costs provided by the operating authority or from schemes of a similar size and nature.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.4	 Anticipated revenue====&lt;br /&gt;
These should be based on the recommendations made regarding tariff structures or provided by the operating authority or regulator.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.5	 Detailed design report====&lt;br /&gt;
A report should accompany the detailed designs, plans and estimates elaborating on the:&lt;br /&gt;
* Engineering aspects,&lt;br /&gt;
* Financial aspects,&lt;br /&gt;
* Administrative aspects, &lt;br /&gt;
* Tender documents &lt;br /&gt;
* Specifications.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.6	 Project write-up to be submitted to potential financiers====&lt;br /&gt;
Each Development Partner may have a different pattern of project presentation for financial request. The project document should therefore follow more guidelines as indicated by the financiers or the local funding sources where applicable.&lt;br /&gt;
&lt;br /&gt;
====2.3.5	Project Phasing====&lt;br /&gt;
Sometimes the implementation of a project is carried out in phases due to among other things, the following reasons:&lt;br /&gt;
* Financial resources available,&lt;br /&gt;
* Opportunity cost of money,&lt;br /&gt;
* Economies of scale,&lt;br /&gt;
* Growth rate in the area,&lt;br /&gt;
* Rate of development in the area,&lt;br /&gt;
* The design (working) life of various installations,&lt;br /&gt;
* Development in levels of service,&lt;br /&gt;
* New technology or method that needs piloting before rolling it out&lt;br /&gt;
Once the basic design period is decided (usually between 10 and 20 years) and water demand is computed for different years, the different elements can be phased. Exceptions do occur where financial assistance capital is being used and there is fear or a probability that further trunches will not be available just a few years later.&lt;br /&gt;
&lt;br /&gt;
Generally, phasing should be undertaken as follows: &lt;br /&gt;
(i)	Dams, river and spring intakes, should be implemented in a single phase to cover all of the ultimate design demand or the hydrologically calculated water availability. This is particularly significant for dams as flood spillways form an expensive integral part and the need to raise a spillway inlet and deal with the additional energy at its exit is usually very costly.&lt;br /&gt;
(ii)	Boreholes to be constructed in Multiple Phases according to the growth in demand.&lt;br /&gt;
(iii)	Treatment plants and storage tanks to be constructed stepwise or in phases, according to the projected growth in demand.&lt;br /&gt;
(iv)	Mechanical installations to be implemented in Multiple Phases according to the design life of the equipment.&lt;br /&gt;
(v)	Pump houses constructed in a Single Phase with space for additional mechanical plant.&lt;br /&gt;
(vi)	Rising mains and main conduits between units to be constructed to cover the ultimate demand in a single Phase.&lt;br /&gt;
(vii)	Long transmission mains to be constructed as two parallel lines in a single Phase where funds allow or in Two Phases where not. It can be advantageous to dedicate one of two parallel transmission mains to supplying water to the terminal reservoir whilst using the second for a mix of local distribution (daytime) and conveyance to the terminal reservoir (night time).&lt;br /&gt;
(viii)	Distribution systems to be constructed according to the growth in development in Multiple Phases.&lt;br /&gt;
&lt;br /&gt;
===2.3.6	Procurement===&lt;br /&gt;
====2.3.6.1	Preparation of Tender Documents====&lt;br /&gt;
The Procurement Management Unit (PMU) using the approved templates as guided by PPRA documentation undertakes preparation of tender documents. In preparing the tender documents undertaken by PMU, unit rate contract is normally adopted for project components such as intake, delivery mains, distribution system, storage tanks and other appurtenances. For specialized areas like the treatment plants and pumping stations it may be necessary to prepare separate tenders for the supply and installation of such facilities. The superstructure may still be included in the main contract bill of quantities. As much as possible one contract is preferred. The suppliers of such specialized equipment would then be included as sub-contractors of the main contractor. Important documents included in contract documents includes:&lt;br /&gt;
* Letter of Invitation to Tender &lt;br /&gt;
* Instruction to Tenderers &lt;br /&gt;
* General Conditions of Contract&lt;br /&gt;
* Special Conditions of Contract&lt;br /&gt;
* Drawings &lt;br /&gt;
* Specifications &lt;br /&gt;
* Bills of Quantities&lt;br /&gt;
* Tender Forms&lt;br /&gt;
* Security Forms &lt;br /&gt;
* Anti-bribery Pledge&lt;br /&gt;
* Schedule of Additional Information&lt;br /&gt;
* Information Data&lt;br /&gt;
&lt;br /&gt;
====2.3.6.2	Tendering process====&lt;br /&gt;
This process involves use of public procurement act to select service providers as detailed in following steps; &lt;br /&gt;
* Issue of tender documents&lt;br /&gt;
* Submission and receipt of tenders&lt;br /&gt;
* Opening of tenders&lt;br /&gt;
* Evaluation of tenders&lt;br /&gt;
* Award of tender&lt;br /&gt;
* Signing of contract agreement&lt;br /&gt;
&lt;br /&gt;
===2.3.7	Implementation/Construction Stage===&lt;br /&gt;
Construction stage includes contract management, Contract supervision and administration.&lt;br /&gt;
====2.3.7.1	Contract Management====&lt;br /&gt;
Contract management entails the following;&lt;br /&gt;
* Contract Management Plan (CMP),&lt;br /&gt;
* Contract Delivery Follow-up,&lt;br /&gt;
* Work progress monitoring &amp;amp; control,  &lt;br /&gt;
* All projects executed must have a completion report (as constructed built reports and drawings). It is essential that Engineers or Foremen keep an up to date record of all project activities including all changes to the original design with reasons for this clearly indicated as well as the approving authority.&lt;br /&gt;
* Initial and Final Acceptance of the Works&lt;br /&gt;
* Contract Close Out&lt;br /&gt;
====2.3.7.2	Contract supervision and administration ====&lt;br /&gt;
During construction stage, it is necessary to consider the following;&lt;br /&gt;
* Each phase of the project implementation should be planned in detail using techniques such as the Critical Path Method (CPM) or Programme Evaluation or/and Review Technique (PERT ) to ensure time control,&lt;br /&gt;
* Work together with the Contractor to prepare a Quality Assurance Plan which shall narrate the scope of the works and the expected quality requirements for the project, the role of the participants in ensuring quality requirements are met&lt;br /&gt;
* Obtain a cash flow forecast from the contractor, and make the Client aware of his payment obligations based on the forecast&lt;br /&gt;
* Keep a close track of all contractors approved claims and adjust the contract price to reflect increase or decrease in the contract price&lt;br /&gt;
* Detailed information in procurement, contract management, contract supervision and administration is detailed well in chapter three and four of Volume III Construction Supervision for Water Supply and Sanitation Projects.&lt;br /&gt;
&lt;br /&gt;
===2.3.8	Operation and Maintenance Stage===&lt;br /&gt;
   This process takes over after the project completion, it involves;&lt;br /&gt;
* Preparation of O&amp;amp;M Plan,&lt;br /&gt;
* Development of Individual Unit Plans for O&amp;amp;M,&lt;br /&gt;
* Plan for capacity Building of O&amp;amp;M Personnel,&lt;br /&gt;
* Plan for Providing Spares and Tools,&lt;br /&gt;
* Plan for Water Audit and Leakage Control,&lt;br /&gt;
* Plan for Efficient Use of Power,&lt;br /&gt;
* Plan for sound financial management system,&lt;br /&gt;
* Plan for Information Education Communication for Water and Sanitation Services,&lt;br /&gt;
* Reports and Record Keeping,&lt;br /&gt;
* Develop appropriate maintenance schedule and check lists,&lt;br /&gt;
* Utilize Standard Operating Procedures,&lt;br /&gt;
* Utilize Water Safety Plans.&lt;br /&gt;
&lt;br /&gt;
Detailed information on planning for operation and maintenance is found in chapter three and four of Volume IV Operation and Maintenance of Water Supply and Sanitation Projects&lt;br /&gt;
&lt;br /&gt;
===2.3.9	Performance Monitoring===&lt;br /&gt;
The aim of the project is to provide the services uninterrupted. To ensure this, a proper monitoring mechanism of the performance of the project should be prepared. Such a mechanism could include proper procedures for procurement and distribution of spare parts, fuel, replacement, a maintenance programme for the project including personnel at the village, District and if necessary at Regional and National levels also. Likewise a water quality surveillance procedure should be instituted in the framework of the existing mechanism.&lt;br /&gt;
&lt;br /&gt;
==2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans==&lt;br /&gt;
It is imperative that during planning of the water supply and sanitation project, designer should consult the Integrated Water Resources Management and Development (IWRMD) plan for a basin where the project is planned to be executed. The development of an IWRMD Plan is a key objective of the water resources component of the Water Sector Development Programme 2006-2025. It is a legal requirement provided for in the Water Resources Management Act, No. 11 of 2009. The plan provides a blueprint for sustainable development and management of the basin’s water resources. &lt;br /&gt;
&lt;br /&gt;
Thus, a water supply and sanitation project designer is advised and encouraged to consult IWRMD plans as they provide:&lt;br /&gt;
&lt;br /&gt;
* The status of water resource availability (both quantity and quality) in the basin,&lt;br /&gt;
* Water data and information necessary for the design of the projects,&lt;br /&gt;
* Framework for water allocations among its competing demands,&lt;br /&gt;
* Water demand for water related sectors,&lt;br /&gt;
* Stakeholders consultation plan.&lt;br /&gt;
&lt;br /&gt;
===2.4.1	Status of Development and Implementation of IWRMD Plans===&lt;br /&gt;
By the time of development of this DCOM manual, IWRMD plans had been developed for six (6) out of the nine basins. The six basins are:&lt;br /&gt;
* Rufiji River Basin,&lt;br /&gt;
* Ruvuma and Southern Coast Basin,&lt;br /&gt;
* Lake Tanganyika Basin,&lt;br /&gt;
* Lake Nyasa Basin,&lt;br /&gt;
* Internal Drainage and&lt;br /&gt;
* Lake Rukwa Basin&lt;br /&gt;
&lt;br /&gt;
It was reported that the development of IWRMD plans for Lake Victoria Basin and Wami/Ruvu basins were on-going. &lt;br /&gt;
&lt;br /&gt;
IWRMD plans implementation challenges have been observed in some basins. These include:&lt;br /&gt;
&lt;br /&gt;
* Inadequate funding to implement plans recommendations,&lt;br /&gt;
* Some plans are not implementable because of including unrealistic recommendations,&lt;br /&gt;
* Some plans are considered to have been more of studies rather than plans,&lt;br /&gt;
* Inadequate human resources capacity to implement them,&lt;br /&gt;
* As required by EMA, ESIAs have not been conducted, contrary to the requirement&lt;br /&gt;
&lt;br /&gt;
===2.4.2	Components of IWRMD Plans===&lt;br /&gt;
The developed IWRMD plans are expected to have the following main components:&lt;br /&gt;
* Component 1: Inventory and review of water availability, use and demand,&lt;br /&gt;
* Component 2: Institutional, Policy and legal framework,&lt;br /&gt;
* Component 3: Sector/Thematic Water Plans,&lt;br /&gt;
* Component 4: Integrated Water Resources Management and Development Plan, &lt;br /&gt;
* Component 5: IWRMD Plan Implementation Strategy and Action Plan.&lt;br /&gt;
&lt;br /&gt;
The production capacity of a source is very important in planning a water supply system. An estimate of the water that can be reliably produced by a water source like a well or spring gives the planner a basis to decide for or against its development. For the source(s) to be considered adequate, they must at least satisfy the maximum daily demand of the area to be served.&lt;br /&gt;
&lt;br /&gt;
==2.5		Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change ==&lt;br /&gt;
&lt;br /&gt;
Water Safety Plan (WSP) is the most effective means of consistently ensuring the safety of a drinking-water supply through the use of a comprehensive risk assessment and risk management approach that encompasses all steps in water supply from the catchment to the consumer (WHO, 2017). The approach enables the operators and managers of water utilities to know the system thoroughly, identify where and how problems could arise, put multiple barriers and management systems in place to stop the problems before they happen and making all parts of the system work properly so as to ensure the safety and acceptability of a drinking water supply intended for human consumption and other domestic uses as summarized in the WHO safe water chain frameworks.&lt;br /&gt;
&lt;br /&gt;
Thus, during the planning phase, a designer should consult guidelines for the preparation of Water Safety Plans - Resilient to Climate Change, which has been prepared and published by Ministry of Water (MoW, 2015)&lt;br /&gt;
&lt;br /&gt;
==2.6	Environmental and Social Impact Assessment Compliance==&lt;br /&gt;
Section 81 of the Environmental Management Act (Cap 191) requires all developers of projects identified in the 3rd Schedule of the Act and detailed in the 1st Schedule of the Environmental Management (Environmental Impact Assessment And Audit) (Amendment) Regulations, 2018, to undertake Environmental Impact Assessment (EIA). Section 82 of EMA (Cap 181) requires that the EIA be carried out prior to the commencement or financing of the project. Procedures for carrying out the EIA, identified under the EIA and Audit  (Amendment) Regulations of 2018 identify eight steps to be followed. According to EIA and Audit (Amendment) Regulations of 2018, projects are classified into the following categories, namely:&lt;br /&gt;
&lt;br /&gt;
(a) “A” category for Mandatory projects;&lt;br /&gt;
 (b) “B1” category for Borderline Project;&lt;br /&gt;
(c) “B2” category for Non-Mandatory; and&lt;br /&gt;
(d) “Special Category&lt;br /&gt;
&lt;br /&gt;
So it is imperative that a proponent and developer of any water supply and sanitation project categorizes their project prior to actual project implementation for the same.&lt;br /&gt;
&lt;br /&gt;
===2.6.1	Procedures for Conducting ESIA in Tanzania===&lt;br /&gt;
Procedures for carrying out the ESIA, identified under the EIA and Audit (Amendment) Regulations of 2018 identify eight key steps to be followed in the EIA process in Tanzania. These are:&lt;br /&gt;
&lt;br /&gt;
* Step 1: Registration,&lt;br /&gt;
* Step 2: Screening, &lt;br /&gt;
* Step 3: Scoping,&lt;br /&gt;
* Step 4: Environmental Assessment,&lt;br /&gt;
* Step 5: Review,&lt;br /&gt;
* Step 6: Recommendations of the Technical Advisory Committee (TAC),&lt;br /&gt;
* Step 7: Submission To The Minister For Environment,&lt;br /&gt;
* Step 8: Approval of the EIS.&lt;br /&gt;
&lt;br /&gt;
It is recommended to consult NEMC guidelines and Environmental Management (Environmental Impact Assessment And Audit) (Amendment) Regulations, 2018 for more details. Also, the following Ministry of Water guidelines, accessible at have to be consulted.&lt;br /&gt;
a)	Guidelines of Good Environmental and Social Practices (GGESP) of July 2019,&lt;br /&gt;
b)	Environmental and Social Management Framework (ESMF) of July 2019.&lt;br /&gt;
&lt;br /&gt;
===2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance===&lt;br /&gt;
&lt;br /&gt;
Section 105 part (2) of the Environmental Act requires that wherever there is a major water project planned for construction, the Ministry responsible for water should conduct Strategic Environmental and Social Assessment. The strategic environmental assessment shall asses the area marked for development and include:&lt;br /&gt;
&lt;br /&gt;
* Baseline environmental conditions and status of natural resources,&lt;br /&gt;
* Identification of ecological sensitive and protected areas,&lt;br /&gt;
* Identification and description of communities around the area,&lt;br /&gt;
* Existing social-economic conditions,&lt;br /&gt;
* Existing economic activities and infrastructure.&lt;br /&gt;
The strategic environmental and social assessment shall be submitted to the Minister responsible for Environment for approval before the planning process.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
==2.7	Potential Impacts of Climate Change on Water Supply Projects==&lt;br /&gt;
It should be emphasized that immediately the project is conceived, hydrological, rainfall and other meteorological data collection must be initiated. In addition and given the long design life of such structures, consideration must be given to the possible impacts of climate change. Detailed account of predictions and impacts of climate change on water supply projects is provided in Appendix A.&lt;br /&gt;
&lt;br /&gt;
URT (2019) has recommended strategies and plans to adapt risks from climate change. The design related strategies of infrastructure, which a designer should consider while planning for water supply projects include:&lt;br /&gt;
&lt;br /&gt;
* Where possible, have at least two sources of supply at different locations. Build superstructures above high flood-line level.&lt;br /&gt;
* Adopt energy-efficiency programmes and, where possible, select facilities which require less power consumption.&lt;br /&gt;
* Monitor wells near coastlines to prevent salinization. If climate change causes sea levels to rise dramatically, even aquifers that have been sustainably utilized can suffer salinization.&lt;br /&gt;
* Utilize renewable energy sources.&lt;br /&gt;
&lt;br /&gt;
Guidelines for resiliency to climate change for urban water supply utilities have been published by the Ministry of Water. &lt;br /&gt;
&lt;br /&gt;
==2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages==&lt;br /&gt;
As explained in detail in section 2.1 of this volume, the CBWSOs have to  be involved in the complete life cycle of the project including ensuring their sustainability during operation and maintenance of the projects under the overall coordination of WSSAs and RUWASA.&lt;br /&gt;
&lt;br /&gt;
==2.9	References==&lt;br /&gt;
Asadieh, B. and Krakauer, N.Y. (2016). Impacts of changes in precipitation amount and distribution on water resources studied using a model rainwater harvesting system. J. Am. Water Resour. Assoc. 52: 1450–1471.https://doi.org/10.1111/ 1752-1688.12472.&lt;br /&gt;
&lt;br /&gt;
Gebrechorkos, S. H., Hülsmann, S., &amp;amp; Bernhofer, C. (2019). Regional climate projections for impact assessment studies in East Africa. Environmental Research Letters, 14(4), 044031. https://doi.org/10.1088/1748-9326/ab055a&lt;br /&gt;
&lt;br /&gt;
Giannini, A., M. Biasutti, I. Held, and A. Sobel (2008). A global perspective on African climate. Clim. Change, 90: 359–383.&lt;br /&gt;
&lt;br /&gt;
Hansingo, K., and C. Reason (2008). Modelling the atmospheric response to SST dipole patterns in the South Indian Ocean with a regional climate model. Meteorol. Atmos. Phys., 100: 37–52.&lt;br /&gt;
&lt;br /&gt;
Hansingo, K., and C. Reason (2009). Modelling the atmospheric response over southern Africa to SST forcing in the southeast tropical Atlantic and southwest subtropical Indian Oceans. Int. J. Climatol., 29: 1001–1012.&lt;br /&gt;
&lt;br /&gt;
Hermes, J., and C. Reason (2009). Variability in sea-surface temperature and winds in the tropical south-east Atlantic Ocean and regional rainfall relationships. Int. J. Climatol., 29: 11–21.&lt;br /&gt;
&lt;br /&gt;
IPCC (2007). Summary for policymakers Climate Change 2007: Impacts, Adaptation and Vulnerability. Contribution of Working Group II to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change ed M L Parry, O F Canziani, J P Palutikof, P J van der Linden and C E Hanson (Cambridge: Cambridge University Press) pp 7-22.&lt;br /&gt;
&lt;br /&gt;
IPCC (2014). Climate Change 2014: Summary for Policymakers, Synthesis Report. Contribution of Working Groups I, II and III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change [Core Writing Team, R.K. Pachauri and L.A. Meyer (eds.)]. IPCC, Geneva, Switzerland, 151 pp.&lt;br /&gt;
&lt;br /&gt;
Li, J., Chen, Y.D., Gan, T.Y., Lau, N. (2018). Elevated increases in human-perceived temperature under climate warming. Nat. Clim. Chang. 8: 43–47. https://doi.org/10.1038/s41558-017-0036-2.&lt;br /&gt;
&lt;br /&gt;
Marchant, R., C. Mumbi, S. Behera, and T. Yamagata (2007). The Indian Ocean dipole—the unsung driver of climatic variability in East Africa. Afr. J. Ecol., 45: 4–16.&lt;br /&gt;
&lt;br /&gt;
Moss, R. H. et al. (2010). The next generation of scenarios for climate change research and assessment. Nature, Vol 463, 11 February 2010, doi:10.1038/nature08823.&lt;br /&gt;
&lt;br /&gt;
Pohl, B., N. Fauchereau, C. Reason, and M. Rouault (2010). Relationships between the Antarctic Oscillation, the Madden - Julian Oscillation, and ENSO, and Consequences for Rainfall Analysis. J. Clim., 23: 238–254.&lt;br /&gt;
&lt;br /&gt;
Rouault, M., P. Florenchie, N. Fauchereau, and C. Reason (2003). South East tropical Atlantic warm events and southern African rainfall. Geophys. Res. Lett., 30, doi:10.1029/2002GL014840.&lt;br /&gt;
&lt;br /&gt;
UNFCCC (2010). The Cancun Agreements. United Nations Framework Convention on Climate Change http://unfccc.int/meetings/cancunnov2010/meeting/6266.php, 2010.&lt;br /&gt;
&lt;br /&gt;
URT (2019). Water sector development programme. Environmental and social management framework (ESMF). Revised version. Ministry of Water.&lt;br /&gt;
&lt;br /&gt;
Vautard, R., Gobiet, A., Sobolowski, S., Kjellström, E., Stegehuis, A., Watkiss, P., Mendlik. T., Landgren, O., Nikulin, G., Teichmann, C. and Jacob, D. (2014). The European climate under a 2°C global warming. Environ. Res. Letters. Environ. Res. Lett. 9, 034006, doi:10.1088/1748-9326/9/3/034006.&lt;br /&gt;
&lt;br /&gt;
Vigaud, N., Y. Richard, M. Rouault, and N. Fauchereau (2009). Moisture transport between the South Atlantic Ocean and southern Africa: Relationships with summer rainfall and associated dynamics. Clim. Dyn., 32: 113–123.&lt;br /&gt;
&lt;br /&gt;
WHO (2017). Climate-resilient water safety plans: Managing health risks associated with climate variability and change. World Health Organization. ISBN: 978-92-4-151279-4. Retrieved from: https://www.who.int/water_sanitation_health/publications/climate-resilient-water-safety-plans/en/&lt;br /&gt;
&lt;br /&gt;
Previous Page: [[Chapter One: Introduction|Chapter One: Introduction]] &amp;lt;&amp;lt;  &amp;gt;&amp;gt; Next Page: [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]]&lt;/div&gt;</summary>
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		<title>Chapter Three: Water Sources Analysis</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=Chapter_Three:_Water_Sources_Analysis&amp;diff=522"/>
		<updated>2020-03-31T11:20:21Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;Water source forms one single most important element and is a key to proper function and thus sustainability of any water supply project. Evidence shows that whenever proper water source analysis has not been adequately conducted, most of water supply projects fall into dysfunction. Thus, this chapter presents the analysis of water sources. It includes analysis of both surface and ground water. Further, the chapter gets into 'nitty gritty' of each of this category.&lt;br /&gt;
&lt;br /&gt;
&amp;lt;div class=&amp;quot;noautonum&amp;quot;&amp;gt;__TOC__&amp;lt;/div&amp;gt;&lt;br /&gt;
&lt;br /&gt;
=Chapter Three: Water Sources Analysis=&lt;br /&gt;
&lt;br /&gt;
==3.1	Availability of Water Resources in Tanzania Mainland==&lt;br /&gt;
Tanzania mainland is endowed with a wide range of water resources that includes the main drainage systems, river basins and natural wetlands that are identified in the next paragraphs. With respect to the drainage systems of water resources in Tanzania mainland, it is divided into five drainage systems that include:&lt;br /&gt;
* The Indian Ocean drainage system,&lt;br /&gt;
* The Internal drainage system to Lake Eyasi, Natron and Bubu depression,&lt;br /&gt;
* The Internal drainage systems to Lake Rukwa,&lt;br /&gt;
* The Atlantic Ocean drainage system through Lake Tanganyika, &lt;br /&gt;
* The Mediterranean Sea drainage system through Lake Victoria.&lt;br /&gt;
&lt;br /&gt;
The drainage systems in turn consist of nine river basins with some bearing names resembling the drainage systems. These nine basins are indicated in Figure 3.1.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
 &lt;br /&gt;
&lt;br /&gt;
Figure 3.1: The River Basins of Tanzania (Source: NWSDS, 2008)&lt;br /&gt;
&lt;br /&gt;
Legend for Figure 3.1&lt;br /&gt;
&lt;br /&gt;
(I) Pangani River Basin	(V) Lakes Nyasa Basin&lt;br /&gt;
(II) Wami/Ruvu River Basin	(VI) Internal Drainage Basin&lt;br /&gt;
(III) Rufiji River Basin	(VII) Lake Rukwa Basin&lt;br /&gt;
(IV) Ruvuma and South Coastal River Basin	(VIII) Lake Tanganyika Basin&lt;br /&gt;
(IX) Lake Victoria Basin&lt;br /&gt;
	&lt;br /&gt;
From geographical point of view, Tanzania is a party to at least eleven transboundary water resources in form of Lakes and Rivers (NWSDS, 2008). These include the following:&lt;br /&gt;
&lt;br /&gt;
* Lake Victoria,&lt;br /&gt;
* Lake Tanganyika,&lt;br /&gt;
* Lake Nyasa,&lt;br /&gt;
* Lake Chala,&lt;br /&gt;
* Lake Jipe,&lt;br /&gt;
* Kagera River,&lt;br /&gt;
* Mara River,&lt;br /&gt;
* Pangani River,&lt;br /&gt;
* Umba River,&lt;br /&gt;
* Ruvuma River and&lt;br /&gt;
* Songwe River.&lt;br /&gt;
&lt;br /&gt;
With its numerous water bodies, Tanzania is perceived to have abundant surface and groundwater resources for meeting its present consumptive and non-consumptive needs. However, the reality is that severe and widespread water shortages exist in many areas of Tanzania because of climate variability, poor distribution of the resource in terms of time and space, and inadequate management of the water resources (NWSDS, 2008). As a result, Tanzania experiences frequent and intense water shortages and some water use conflicts.&lt;br /&gt;
&lt;br /&gt;
Furthermore, Tanzania is relatively dry with more than half of the country receiving, on average, less than 800 mm of rainfall per year depending upon air circulation patterns and the movement of the convergence zones in the region. The semi-arid Central and Northern parts of the country, including areas immediately South of Lake Victoria receive less than 700 mm of rainfall per annum and are dry for an average of seven consecutive months a year. River flows in these areas are intermittent. In the Southern, Western and Northern highlands, which receive more than 1,000 mm/year of rainfall, rivers are perennial, and some of these experience frequent floods.&lt;br /&gt;
 &lt;br /&gt;
As an example, in 1999 the availability of renewable freshwater resources, both surface and groundwater was estimated  to be about 2,700 m3/capita/year. By 2018, this estimate was reduced to 2,330 m3/capita/year due to increased population alone.  The average figure is significantly above the level of 1,700 m3/capita/year set by the United Nations as denoting water stress, or 1,000 m3/capita/year denoting water scarcity. Furthermore, due to the projected population growth alone, Tanzania's annual freshwater renewal rate is projected to drop to 1,500 m3/capita/year by 2025, thus categorising the country as being water stressed by then. &lt;br /&gt;
&lt;br /&gt;
On the whole, Tanzania has sufficient surface and ground water resource potential to meet most of her present needs.  However, differences in topography, rainfall patterns and climate account for the existing variation in the availability of water in different parts of the country.  In the densely populated Pangani and Rufiji Basins, these variations have already resulted into water stress.  It is estimated that the annual surface runoff from Tanzania to the world’s oceans is about 74 x 109 m3. The Rufiji, which drains a 177,000 km2 area, contributes over 50% of the runoff3. Typical annual runoffs are shown in the Table 3.1 for some of the major rivers of Tanzania. &lt;br /&gt;
&lt;br /&gt;
Table 3.1 Mean annual river discharges for some of the principal rivers of Tanzania&lt;br /&gt;
River 	Mean Annual Discharge (Million m3/yr) &lt;br /&gt;
Rufiji (at Steiglers Gorge) 	22,250 &lt;br /&gt;
Kilombero (at Swero) 	14,470 &lt;br /&gt;
Malagarasi (at Taragi Ferry) 	5,060 &lt;br /&gt;
Ruvu (at Moro Bridge) 	1,370 &lt;br /&gt;
Wami (at Mandera) 	3,280 &lt;br /&gt;
Ruhuhu (at Kikonge) 	5,600 &lt;br /&gt;
Kiwira (at Kyela) 	1,900 &lt;br /&gt;
Kagera (at Kyaka) 	7,064 &lt;br /&gt;
Mara (at Mara Mines) 	1,971 &lt;br /&gt;
Pangani (at Hale) 	627 &lt;br /&gt;
(Source: NWSDS, 2008)&lt;br /&gt;
 &lt;br /&gt;
&lt;br /&gt;
The most abundant surface water resources exist in Lakes Victoria, Tanganyika, Nyasa, Chala and Jipe, as well as the Kagera, Mara and Songwe rivers, which are trans-boundary waters. The use of these abundant surface water resources for water supply, irrigation and other purposes is still very limited even today.&lt;br /&gt;
&lt;br /&gt;
Tanzania is also rich in wetland systems that are areas which, for part of the year, have enough water to enable the development of types of plants and animals adapted to these conditions.  These include the lakes of the Western and Eastern Rift Valley system, Lake Victoria, numerous small lakes, riverine flood plains and permanent swamps, coastal mangrove and deltaic systems, and a number of artificial impoundments and reservoirs and fish ponds.  There are numerous permanent and seasonal freshwater swamps and flood plains distributed in almost all of the country's major drainage basins, which account for some 2.7 million hectares.  The largest in this category are found in the Rufiji/Ruaha river system and in the Malagarasi/Moyowosi system, while other river systems are the Kagera River, along with Ugalla River, Suiwe River, Mara River, Pangani, Wami and Ruvu Rivers. The principal wetlands of Tanzania constitute one of the country's richest and most durable resources. &lt;br /&gt;
&lt;br /&gt;
==3.2	Water Sources Available in Tanzania Mainland==&lt;br /&gt;
In Tanzania, there are three main categories of water sources available, namely rainwater, surface and groundwater. &lt;br /&gt;
&lt;br /&gt;
===3.2.1	Rainwater and fog harvesting===&lt;br /&gt;
One of sources of water include rainwater and fog that can generate limited amounts of very clean water if they are properly collected and stored. In an area where other water sources are not available, consideration should be given to harvesting rainwater and fog.&lt;br /&gt;
&lt;br /&gt;
===3.2.2	Surface Water===&lt;br /&gt;
For design purposes, the surface water sources that can be considered include;&lt;br /&gt;
* Rivers or streams,&lt;br /&gt;
* Impoundments (Reservoirs and ponds),&lt;br /&gt;
* Springs,&lt;br /&gt;
* Lakes,&lt;br /&gt;
* Dams (charco, sand, earth etc).&lt;br /&gt;
&lt;br /&gt;
A brief description of each water source is provided below.&lt;br /&gt;
&lt;br /&gt;
3.2.2.1	 Rivers or streams &lt;br /&gt;
Rivers and streams are water sources that originate from springs located in highlands which flow down to the end of the respective drainage basin which can be lakes, seas or oceans as depicted on the map of Tanzania in Figure 3.1. &lt;br /&gt;
3.2.2.2	 Impoundments&lt;br /&gt;
Impoundments includes all types of reservoirs that emanate from road borrow pits, mining, human or natural activities that are utilised as sources of water for a formal water supply project. &lt;br /&gt;
3.2.2.3	 Springs&lt;br /&gt;
Springs include artesian or freely flowing spring water that has been tapped by an intake structure to facilitate supply of water to a designated community. Spring is a point where groundwater flows out of the ground, and is thus where the aquifer surface meets the ground surface. A spring may be ephemeral (intermittent) or perennial (continuous). Springs can be developed by enlarging the water outlet and constructing an intake structure for water catchment and storage. &lt;br /&gt;
&lt;br /&gt;
3.2.2.4	Lakes &lt;br /&gt;
Lakes found in Tanzania are either located at the end of drainage basins or are highland lakes and some of them are volcanic lakes. Tanzania is endowed with many small inland lakes apart from the third biggest lake in the world (Lake Victoria) as well as Lake Tanganyika which is the world’s deepest lake. Both lakes supply water to various localities around their respective catchments.&lt;br /&gt;
3.2.2.5	 Dams &lt;br /&gt;
Dams are classified based on the availability of construction materials. Various types of dams can be built ranging from earth fill dams, concrete dams, sand dams and charco dams. These are purposely built structures that allow impoundment of river and/or rain water for various end uses. &lt;br /&gt;
&lt;br /&gt;
3.2.3	Groundwater&lt;br /&gt;
Groundwater is that portion of rainwater which has percolated beneath the ground surface to form an underground reservoir referred to as aquifer water. The upper surface of groundwater is the water table. Groundwater is often clear, free from organic matter and bacteria due to the filtering effect of the soil on water percolating through it. However, groundwater almost always contains dissolved minerals from the soil. Groundwater is often better in terms of quality than surface waters. It is less expensive to develop for use, and usually provides more adequate supply in many areas in the country. In semi-arid and the drier parts of the country,  groundwater has played and will continue to play a major role as the sole water source for various uses especially in the central and northern parts of the country and the drier regions of Dodoma, Singida, Shinyanga, Tabora, Mwanza, Mara, Arusha, Coast and Southern Kilimanjaro.&lt;br /&gt;
&lt;br /&gt;
Groundwater can be considered as either spring water or well (or borehole) water. Springs, offer excellent water supply opportunities, but are generally found in hilly or mountainous areas only. They may require long pipelines in order to bring the water to the demand area. This is a feasible source for larger and concentrated settlements but rarely for dispersed populations. For rural water supply systems, groundwater is generally preferred as a water source. &lt;br /&gt;
&lt;br /&gt;
The main sub-types of groundwater and extraction methods are as follows:&lt;br /&gt;
&lt;br /&gt;
3.2.3.1	 Infiltration galleries/wells &lt;br /&gt;
Infiltration galleries are horizontal wells, constructed by digging a trench into the water-bearing sand and installing perforated pipes in it. Water collected in these pipes converges into a “well” from which it is pumped out. &lt;br /&gt;
3.2.3.2	 Well&lt;br /&gt;
This is a hole constructed by any method such as digging, driving, boring, or drilling for the purpose of extracting water from underground aquifers. Wells can vary greatly in depth, water volume and water quality. Well water typically contains more minerals in solution than surface water and may require treatment to soften the water by removing minerals such as arsenic, iron and manganese. Well water may be drawn by pumping from a source below the surface of the earth. Alternatively, it could be drawn up using containers, such as buckets that are raised mechanically or by hand.&lt;br /&gt;
&lt;br /&gt;
Wells are various types of artificially constructed water production wells that are designated as shallow wells (up to 20 metres deep) or deep wells (more than 20 metres deep) as designated by the Ministry responsible for water from time to time.  Water is pumped out of the well into the end user containers or a storage tank using various types of pumps that can be driven manually or using various energies. Typical cross sections through such wells are given in Section 3.6.5.&lt;br /&gt;
3.2.3.3	Classification of wells based on the aquifer tapped&lt;br /&gt;
As mentioned, an aquifer contains a considerable amount of groundwater underground beneath layers of permeable soil material like sand or gravel. Aside from their water storage capacity, aquifers allow the underground flow of groundwater. Aquifers are recharged with rainwater that seeps down to the soil and through the permeable layers.&lt;br /&gt;
3.2.3.3.1	Shallow wells&lt;br /&gt;
Generally, a well is considered shallow if it is less than 20 metres deep. Shallow wells tap the upper water-bearing layer underground. This permeable layer, however, usually has limited safe yield due to its great dependence on seasonal rainfalls. Therefore, the supply capacity of shallow wells could be unreliable and are sometimes intermittent. Also, the water extracted from the upper strata is usually more affected by contamination since the aquifer being tapped is near the ground surface where possible sources of contamination are abound. Protection against contamination is therefore one of the main considerations in constructing a shallow well.&lt;br /&gt;
3.2.3.3.2	Deep wells&lt;br /&gt;
Deep wells, which are over 20 metres deep, tap the deeper unconfined aquifer. This aquifer is not confined by an overlying impermeable layer and is characterized by the presence of a water table. A deep well is less susceptible to surface contamination because of the deeper aquifer. Also, its yield tends to be more reliable since it is less affected by seasonal precipitation.&lt;br /&gt;
&lt;br /&gt;
3.2.3.3.3	Artesian wells&lt;br /&gt;
Artesian wells are much like the deep wells except that the water extracted is from a confined aquifer. The confining impermeable layers are above and below the aquifer. Groundwater recharge enters the aquifer through permeable layers at high elevations causing the confined groundwater at the lower elevations to be under pressure. In some cases, the hydraulic pressure of the aquifer is sufficient for a well to flow freely at the well head.&lt;br /&gt;
&lt;br /&gt;
3.3	Quality Suitability of Water Sources for Water Supply Projects&lt;br /&gt;
When considering the different water sources for water supply projects, it is necessary to ensure that the quality of the water source expected to be utilised is monitored well preferably for a period of not less than three years consecutively to ensure the variability of the quality is captured during the wet and dry seasons. When one looks at the list of the potential sources presented in the foregoing section, such a monitoring programme may not be necessary for rainwater and fog. Only short-term monitoring of the quality of these two sources should be undertaken.&lt;br /&gt;
&lt;br /&gt;
3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment&lt;br /&gt;
&lt;br /&gt;
A decision on whether the water source needs to be subject to water treatment or otherwise will emanate from the results of the short term tests on the quality of the water which will in turn guide the decision of pilot testing the recommended flow sheets particularly for river/streams, lakes, impoundments and dams. Groundwater will usually need only a few unit operations for removal of the identified elevated impurities that may include Iron, Manganese or Fluoride and the need to disinfect water from shallow wells in addition to maintaining residual disinfectants for prevention of re-contamination. Rainwater and condensates from fog will not need to be pilot tested.&lt;br /&gt;
&lt;br /&gt;
3.5	General Considerations for Selection of Water Sources &lt;br /&gt;
In the selection of a source or sources of water supply, adequacy and reliability of the available supply can be considered as the overriding criteria. Without these, the water supply system cannot be considered viable. These, together with the other factors that should be considered (and which are interdependent), are as follows:&lt;br /&gt;
&lt;br /&gt;
3.5.1	Adequacy and reliability&lt;br /&gt;
Adequacy of water supply requires that the quantity of water flow of water source be large enough to meet present and future water demand. On the other hand, source reliability can be expressed by how frequently a water system expects normal demand to go unmet, such as a one-in -25 year or even a one-in-50 year drought. Safe yield is a 1-day low flow rate that is exceeded for 96 percent of the period of record and that can be related to the determined average daily water demand in order to establish the reliability of a water source. For a river/stream, safe yield represents the minimum flow rate that will guarantee no risk to the river hydrology and its surroundings. Safe yield is estimated so as to check whether the planned withdrawal for water supply purposes will be met. To determine the safe yield of a river or stream, a flow -frequency/probability analysis presented in section 3.1.5.5 should be performed. From the analysis, the determined 96 % low flow index should be taken as the safe yield of the river or stream and thus considered as the water source reliability.&lt;br /&gt;
&lt;br /&gt;
3.5.2	Quality of water sources&lt;br /&gt;
The assessment of water quality of a water source is important to establish the suitability of water source for human consumption. The quality of surface water is determined by the amount of pollutants and contaminants picked up by the water in the course of its travel. While flowing over the ground, surface water collects silt, decaying organic matter, bacteria and other micro-organisms from the soil. Sources which require little or no treatment of the water should be chosen in the first instance, provided the required quantity of water can be obtained. Hence springs and ground water resources should always be exploited in the first hand. Surface water from rivers, streams and lakes will almost always require some treatment to render it safe for human consumption. However, for large supplies, surface water will often still be the most economical alternative. Rivers which have the bulk of their catchments in forest areas should be preferred.&lt;br /&gt;
&lt;br /&gt;
Thus, all surface water sources should be presumed to be unsafe for human consumption without some form of treatment. The option to treat surface water to make it safe for human consumption in compliance with the latest edition of Tanzania potable water standards (TBS, TZS 789) has to be evaluated to decide on the feasibility of the water supply project.&lt;br /&gt;
&lt;br /&gt;
3.5.3	Technical Requirements&lt;br /&gt;
The development of the source should be technically feasible, the operation and maintenance requirements for the source abstraction and supply system should be appropriate to the resources available.&lt;br /&gt;
&lt;br /&gt;
3.5.4	Cost implications to develop a water source&lt;br /&gt;
The assessment of investment costs to develop a given water source including operation and maintenance costs has a bearing in the selection of the water source for development. Affordability of investment costs is an important factor to be considered in the selection of the water source.&lt;br /&gt;
&lt;br /&gt;
3.5.5	Protection of water sources&lt;br /&gt;
The location of a water source is a key factor in securing the highest quality water source. In analysing a source location, the design engineer should consider the measures necessary to protect the water source from human excreta, from industrial discharges and from agricultural run-off. In addition, measures to establish and maintain watershed control, physical protection and barriers to contamination have to be considered to ensure sustainable quantity and quality of the raw water.&lt;br /&gt;
&lt;br /&gt;
3.5.6	Legal and management requirements&lt;br /&gt;
Ownership of the land and the legal requirements of obtaining permission to abstract are also factors to consider when selecting a source. Sources on private land may cause access problems.&lt;br /&gt;
&lt;br /&gt;
3.5.7	Distance of water supply source&lt;br /&gt;
The source of the water supply must be situated as near to the demand area as possible. Hence, less length of pipes needs to be installed and thus economical transfer and supply of water. The source(s) nearest to the demand area is usually selected.&lt;br /&gt;
&lt;br /&gt;
3.5.8	Topography of the project area and its surroundings&lt;br /&gt;
The area or land between the source and the area to be served by water supply system should not be highly uneven, i.e., it should not have steep slopes because cost of construction or laying of pipes is very high in such areas.&lt;br /&gt;
&lt;br /&gt;
3.5.9	Elevation of a source of water supply&lt;br /&gt;
The source of water must be on a high elevation than the demand area so as to provide sufficient residual pressure in the water for daily requirements. When the water is available at lower levels, then pumps are used to pressurize water. This requires an excess developmental and operational tasks and costs.&lt;br /&gt;
&lt;br /&gt;
3.6	Determination of water source yield&lt;br /&gt;
Sources which require little or no treatment of raw water such as springs, wells and boreholes should be given the highest selection priority provided their yields are sufficient to meet the water demands of the water supply scheme. For large supplies, surface water will continue to be the most economical alternative water source. In selecting surface water sources, rivers with upland and mostly forested catchments should be given preference. Sub-surface water drawn from a riverbed or river bank can sometimes be a viable alternative in dry areas with only seasonal flows in the river, or in rivers with a high silt load.&lt;br /&gt;
&lt;br /&gt;
Sources from which water can be supplied by a gravity system are particularly more favourable than those which require pumping with significant energy costs. For household and small community water supplies, rainwater harvesting will be the most appropriate in most medium and high potential areas in Tanzania that receive sufficient rains.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
3.6.1	Rainwater and fog harvesting&lt;br /&gt;
3.6.1.1	 Rainwater harvesting&lt;br /&gt;
Rainwater harvesting is a technique of collection and storage of rainwater into natural reservoirs or tanks, or the infiltration of surface water into subsurface aquifers (before it is lost as surface runoff). Types of rainwater harvesting systems are described in the sections below.&lt;br /&gt;
&lt;br /&gt;
3.6.1.1.1	Types of rainwater harvesting&lt;br /&gt;
Two types of rainwater harvesting should be considered:&lt;br /&gt;
&lt;br /&gt;
•	Land catchment,&lt;br /&gt;
•	Roof catchment.&lt;br /&gt;
&lt;br /&gt;
Important data for design of rainwater harvesting systems:&lt;br /&gt;
•	Rainfall data&lt;br /&gt;
•	Catchment/Surface Area &lt;br /&gt;
•	Run-off Coefficient&lt;br /&gt;
&lt;br /&gt;
To accurately estimate the potential rainwater supply from a catchment, reliable rainfall data for a 10-year period is required . The Hydrology Section, Tanzania Meteorology Agency, and Agriculture Departments should be contacted for rainfall data wherever rainwater-harvesting technology is proposed. &lt;br /&gt;
&lt;br /&gt;
The amount of rainfall collected depends on the surfaces where rain falls and the runoff coefficient K of the surface. The runoff coefficient varies with topography, land use, vegetation cover, soil type and moisture content of the soil. In selecting run off coefficients the future characteristics of the water shed are considered. If land use varies within a water shed consider the segments individually and use a weighted coefficient value to determine the total runoff for the watershed. Practically annual rainfall falls during the rainy seasons between October and May.&lt;br /&gt;
&lt;br /&gt;
(i) Run-off Coefficients&lt;br /&gt;
Table 3:2 shows the runoff coefficients for various surfaces. They should be used for calculating the fraction of the rainfall which can be harvested.&lt;br /&gt;
&lt;br /&gt;
Table 3.2: Run-Off Coefficients for Different Surfaces&lt;br /&gt;
SURFACE	RUN-OFF&lt;br /&gt;
COEFFICIENT (K)&lt;br /&gt;
1.	Roof catchments	&lt;br /&gt;
	•	Roof tiles	0.8 to 0.9&lt;br /&gt;
	•	Corrugated sheets	0.7 to 0.9&lt;br /&gt;
2.	Ground surface covering&lt;br /&gt;
	•	Concreted	0.6 to 0.8&lt;br /&gt;
	•	Bitumen, plastic sheeting, butyl rubber	0.8 to 0.9&lt;br /&gt;
	•	Pavement of stone, bricks with open joints	0.5 to 0.6&lt;br /&gt;
	•	Pavement of stone, bricks with tightly cemented joints	0.75-0.85&lt;br /&gt;
3.	Compacted and smoothened soil	0.3 to 0.5&lt;br /&gt;
4. Lawns, sandy soil&lt;br /&gt;
	•	2% slope	0.05-0.10&lt;br /&gt;
	•	2.7% slope	0.10-0.15&lt;br /&gt;
	•	&amp;gt;7%	0.15-0.20&lt;br /&gt;
5. Lawns, heavy soil&lt;br /&gt;
	•	2% Slope	0.13-0.17&lt;br /&gt;
	•	2.7% slope	0.18-0.22&lt;br /&gt;
	•	&amp;gt;7%	0.25-0.35&lt;br /&gt;
6.	•	Uncovered surface, flat terrain	0.3&lt;br /&gt;
	•	Uncovered surface, slope less than 10%	0.0 to 0.4&lt;br /&gt;
	•	Rocky natural catchments	0.2 to 0.5&lt;br /&gt;
&lt;br /&gt;
3.6.1.1.2	Components of rainwater harvesting system&lt;br /&gt;
a) Catchments Area: The catchment of a water harvesting system is the surface which directly receives the rainfall and provides water to the system.&lt;br /&gt;
b) Coarse mesh at the roof to prevent the passage of debris.&lt;br /&gt;
c) Gutters to collect and transport rainwater to the storage tank. Gutters can be semi-circular or rectangular and could be made using:&lt;br /&gt;
&lt;br /&gt;
•	Locally available material such as plain galvanised iron sheet (20 to 22 gauge), folded to required shapes &lt;br /&gt;
•	Semi-circular gutters of PVC material can be readily prepared by cutting those pipes into two equal semi-circular channels.&lt;br /&gt;
•	Bamboo trunks cut vertically in half&lt;br /&gt;
&lt;br /&gt;
The size of the gutter should be according to the flow during the highest intensity rain. It is advisable to make them 10 to 15 per cent oversize.&lt;br /&gt;
&lt;br /&gt;
d) Conduits/pipeline that carry rainwater from the catchment or rooftop area to the harvesting system. Conduits can be of any material like polyvinyl chloride (PVC) or galvanized iron (GI), materials that are commonly available.&lt;br /&gt;
&lt;br /&gt;
e) First Flush pipe to separate first rainwater contaminants namely debris, dirt, and dust.&lt;br /&gt;
&lt;br /&gt;
3.6.1.1.3	Estimation of the yield&lt;br /&gt;
A first estimate of the average yield of a catchments area can be found using the following expression.&lt;br /&gt;
S = K × I × A						(3.1)&lt;br /&gt;
Where: &lt;br /&gt;
S = Yield in m3 / annum &lt;br /&gt;
A = Area of catchment/surface, m2 &lt;br /&gt;
I = Average annual rainfall m/annum &lt;br /&gt;
K = runoff coefficient &lt;br /&gt;
&lt;br /&gt;
Determination of average runoff coefficient for the entire catchment area composed of different surfaces can be calculated as follows:&lt;br /&gt;
 +...					(3.2)&lt;br /&gt;
The required capacity of the collection facility should be calculated using available meteorological data showing the rainfall pattern of the area. However, for rough calculations the storage tank, capacity may be calculated as follows:&lt;br /&gt;
C = D × T × 10-3						(3.3)&lt;br /&gt;
&lt;br /&gt;
Where:&lt;br /&gt;
C = Capacity of tank in m3 &lt;br /&gt;
D = Total water demand in litres / day&lt;br /&gt;
T = Longest dry spell in days&lt;br /&gt;
&lt;br /&gt;
3.6.2	Hydrological Analysis of Surface Waters&lt;br /&gt;
The Design Manual for Water Supply projects is expected to reflect the best concepts on what constitutes the basis for designing a safe, reliable and sustainable water system. Hydrological principles must be taken into consideration during the feasibility and preliminary design stages of the water supply system to ensure that from the outset, design and construction of the system is done right. The design engineer must apply hydrological principles during design of the water system to ensure that the system being designed does not result in exhausted water supply sources and empty reservoirs after construction of the project is completed. If it is recognised from the beginning that there is water deficiency from the source, then the water source should not be considered for development.&lt;br /&gt;
&lt;br /&gt;
The following steps should be followed when undertaking hydrological analysis for the water supply projects:&lt;br /&gt;
&lt;br /&gt;
Step 1: Measurement of the quantity of surface water sources,&lt;br /&gt;
Step 2: Low flow assessment of surface water sources,&lt;br /&gt;
Step 3: Flood flow estimation,&lt;br /&gt;
Step 4: Rainfall analysis,&lt;br /&gt;
Step 5: Water permit application,&lt;br /&gt;
Step 6: Data to support hydrological analysis.&lt;br /&gt;
&lt;br /&gt;
Step 1: Measurement of River Discharge&lt;br /&gt;
In order to assess the amount of water available from the identified surface water source, a discharge measurement must be carried out during both the dry and wet seasons. Measurement of discharge will highlight the production capacity of a water source, the information which is important in the planning of a water system. An estimate of the quantity of water that can be reliably produced by a water source gives the planner a basis to decide for or against its development. For the sources to be considered adequate, they must at least satisfy the average day water demand of the area to be served by a water system. The average daily water demand is calculated from estimated average water requirements for domestic, commercial, industrial, public institutions and livestock. The following methods can be used to measure discharge.&lt;br /&gt;
&lt;br /&gt;
a) Volumetric Method&lt;br /&gt;
This method is appropriate for measuring small quantities of flow from small streams and springs. Flow can be measured by measuring the volume. The equipment required are a stop watch and a bucket or drum of known volume. The method consists of determining the time required to fill the bucket or drum. For more accurate results, the measurement is repeated several times, and the average time of these trials is taken.&lt;br /&gt;
&lt;br /&gt;
b) V-Notch Weir Method&lt;br /&gt;
A weir is an overflow structure built across an open channel for the purpose of measuring the rate of flow. Weirs may be rectangular, trapezoidal or triangular in shape. The triangular or V-Notch Weir is a flow measuring device particularly suited for small flows. The V-Notch Weir often used in flow measurements is the 90° V-Notch that is placed in the middle of the channel and water is allowed to flow over it. The water level in the channel is then measured using a gauging rod. The zero point in the rod should be level with the sill or crest of weir/notch. For a known height of water above the zero in the rod, the flow in cumecs for the 90° V-Notch can be obtained by using the formula:&lt;br /&gt;
&lt;br /&gt;
 							(3.4)&lt;br /&gt;
&lt;br /&gt;
 								(3.5)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
Q = Discharge in m3/sec&lt;br /&gt;
H =Height of Water level above the crest of the weir in meters&lt;br /&gt;
In this case, the discharge coefficient of the weir is approximated to be equal to 0.58.&lt;br /&gt;
&lt;br /&gt;
c) Current meter Measurement&lt;br /&gt;
The current meter is an instrument that is used to measure relatively larger quantities of flow from streams and rivers. The instrument consists of a propeller rotating freely on a well-lubricated shaft. The device is lowered into the water and the rate of revolution of the impeller is directly proportional to the velocity of the water flow. A small magnet is usually built into the shaft of the instrument and a coil detects the passage of the magnet and allows the number of revolutions of the shaft in the given time to be counted. Once the rate of revolution of the impeller is known the water velocity can be calculated using the calibration equation for the instrument, which is expressed as follows:&lt;br /&gt;
&lt;br /&gt;
 									(3.6)&lt;br /&gt;
&lt;br /&gt;
Where, &lt;br /&gt;
V is the water velocity in meters per second&lt;br /&gt;
n is the number of revolutions of the impeller per second&lt;br /&gt;
a, b are constants for the particular instrument.&lt;br /&gt;
&lt;br /&gt;
The discharge measurement using the current meter at the time of measurement, Q,  is  determined by multiplying the velocity of flow and water flow cross-section area.&lt;br /&gt;
&lt;br /&gt;
Step 2: Low flow assessment&lt;br /&gt;
The assessment of low flow magnitudes of streams/rivers or springs in hydrology is important in the planning of a water supply system in view of the fact that it reflects on the water source adequacy and reliability to meet the consumer demand. In low flow hydrology, two questions are asked about a particular river identified to be a water source for a given water supply system:&lt;br /&gt;
&lt;br /&gt;
(i)	Does the river supply a particular water demand at all times?&lt;br /&gt;
(ii)	If not, how much water must be stored in order to meet any deficiency which may arise?&lt;br /&gt;
&lt;br /&gt;
Techniques of flow duration curves, annual minimum flow analyses and annual drought volumes are applied to address the two questions.&lt;br /&gt;
&lt;br /&gt;
a) Flow duration curve&lt;br /&gt;
The flow-duration curve (FDC) is defined as a cumulative frequency curve that shows the percent of time specified discharges were equalled or exceeded during a given period. It combines in one curve the flow characteristics of a stream throughout the range of discharge, without regard to the sequence of occurrence. To prepare a flow-duration curve, the daily, weekly, or monthly flows during a given period are arranged according to magnitude, and then percent of time during which specified flow values are equalled or exceeded are computed. &lt;br /&gt;
&lt;br /&gt;
A flow duration curve once it is prepared, is used to determine the indices of low flow magnitudes; for example, the 96-percentile flow (Q96), is the flow that is exceeded for 96 percent of the period of record. This discharge value is a useful index of low flow that is related to the quantity of water that can be available for water supply in the dry season.&lt;br /&gt;
&lt;br /&gt;
The following steps are followed to construct the FDC:&lt;br /&gt;
&lt;br /&gt;
(i)	Rank the observed stream flows in descending order (from the maximum to the minimum value).&lt;br /&gt;
(ii)	Calculate exceedance probability (P) of each flow as follows:&lt;br /&gt;
&lt;br /&gt;
		 						(3.7)&lt;br /&gt;
&lt;br /&gt;
		Where,&lt;br /&gt;
			P is the probability that a given flow will be equalled or exceeded 			(% of time),&lt;br /&gt;
			m is the ranked position of a given flow value on the list,&lt;br /&gt;
			n is the length of the sample.&lt;br /&gt;
&lt;br /&gt;
(iii)	 A FDC is obtained by plotting each ordered observed streamflow value versus the corresponding calculated exceedance probability.&lt;br /&gt;
(iv)	 Read the indices of low flow magnitudes from the FDC corresponding to 90%, 95% and 99% probabilities of exceeded.&lt;br /&gt;
&lt;br /&gt;
b) Low flow frequency analysis&lt;br /&gt;
The frequency analysis of low river flows is performed by analyzing 1-day or 7-day or 10-day annual minimum flow series obtained by selecting the lowest flow values occurring in each year of record. The set of observed annual minimum flow values recorded at any gauging station is assumed to be a random statistical sample from the population of all possible annual minima at the given site.&lt;br /&gt;
&lt;br /&gt;
The selected set of observed annual minimum flow values is fitted to the Gumbel statistical distribution and then the annual minimum flow magnitudes (QT) corresponding to the design probability of failure (1/T) is then estimated from the Gumbel prediction equation:&lt;br /&gt;
&lt;br /&gt;
 								(3.8)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
QT = Low flow magnitude&lt;br /&gt;
T = Return period of one failure in T years&lt;br /&gt;
  and  = Gumbel Parameters &lt;br /&gt;
KT = Frequency factor, obtained as:&lt;br /&gt;
&lt;br /&gt;
 							       (3.9)&lt;br /&gt;
&lt;br /&gt;
Results from low flow frequency analysis:&lt;br /&gt;
(i)	If the value of QT is large in comparison to QD, the average day water demand, then the river can be considered to be able to supply the demand satisfactorily.&lt;br /&gt;
(ii)	On the other hand if QT is less than or of the same order of magnitude as, QD, ,then the river alone without some form of flow regulation could not be considered satisfactory for supplying the demand. &lt;br /&gt;
&lt;br /&gt;
c) Annual drought volumes Analysis&lt;br /&gt;
On the basis of the results obtained from low flow frequency analysis, in case the annual minimum flow magnitudes (QT) corresponding to the design probability of failure (1/T) is found to be less than QD, demand flow, then storage will be required to meet the established water demand. The required storage is determined by carrying out deficiency/drought Volumes Analysis.&lt;br /&gt;
&lt;br /&gt;
The storage required on a river to meet a specific demand depends on the following factors:&lt;br /&gt;
&lt;br /&gt;
•	Variability of the river flow&lt;br /&gt;
•	Magnitude of the demand&lt;br /&gt;
•	Degree of reliability of meeting the demand&lt;br /&gt;
&lt;br /&gt;
The capacity of the reservoir required to augment the river flow in any year can  be determined from the analysis of the series of annual maximum deficiencies (drought volumes) as follows:&lt;br /&gt;
&lt;br /&gt;
Drought volumes V1, V2, V3,…, Vn are computed from a hydrometric record of the river flow (Qi), with reference to the demand flow (QD), i.e., (Vi = Qi-QD). &lt;br /&gt;
&lt;br /&gt;
The set of observed annual maximum deficiencies at any gauging station is assumed to be a random statistical sample. The annual maximum deficiency (VT) corresponding to the probability of failure (1/T) is estimated from the series of annual maximum deficiencies using a statistical distribution, e.g., Gumbel distribution as illustrated in previous section. The design storage of the reservoir can be made equal to the volume VT corresponding to a risk of one failure in T years. &lt;br /&gt;
&lt;br /&gt;
Step 3: Dependable Rainfall Analysis&lt;br /&gt;
Rainfall analysis is carried out when the need arises to determine dependable rainfall in a given area for the purpose of designing a rainwater harvesting system for domestic use. Frequency analysis of recorded annual rainfall data from a given area, enables the determination of the 90% dependable annual rainfall. This is the value of rainfall magnitude that will be exceeded 90% of the time. In the design of Rainwater Water Harvesting system, catchment (i.e. roof) area and depth of rainfall are important parameters for estimation of optimal storage size. Taking note of the fact that rainfall amounts vary on a year to year basis, the computed rainfall magnitude that is exceeded 90% of the time, is taken as the value of annual rainfall depth that can be expected to occur with some degree of certainty and thus used in the design. The exceedance probability is determined by ranking the observed annual rainfall in ascending order (from the minimum to the maximum value) and then calculating non-exceedance probability (P) as follows:&lt;br /&gt;
&lt;br /&gt;
 								(3.10)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
P is the probability that a given rainfall will be equalled or not exceeded (% of time),&lt;br /&gt;
m is the ranked position of a given rainfall value on the list,&lt;br /&gt;
n is the length of the sample.&lt;br /&gt;
&lt;br /&gt;
The probability of dependable rainfall is obtained by calculating  the value of exceedance probability (1 – P).&lt;br /&gt;
&lt;br /&gt;
Step 4: Flood flow estimation for intakes and small dams' spillways&lt;br /&gt;
The need to estimate flood peaks or design floods arises where it is required to design a spillway of a dam proposed for water storage and also the design of water intake structures. Water intakes and spillway of small dams are designed to accommodate the 100-year flood. &lt;br /&gt;
&lt;br /&gt;
Frequency analysis of observed Annual Maximum streamflow records from a gauging station enables the estimation of flood peaks. The statistical distribution namely the Gumbel distribution or other statistical distribution used in Tanzania such as Pearson type 3, Log-Pearson type 3, Log-Normal and General Extreme Value can be used to carry out frequency analysis in order to determine the magnitude of flood peak of 100-year required for the design. The estimation of design flood peak magnitudes for specified return periods using the Gumbel Distribution is illustrated below.&lt;br /&gt;
&lt;br /&gt;
Prediction equation&lt;br /&gt;
&lt;br /&gt;
 								(3.11)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
QT = Flood peak magnitude&lt;br /&gt;
T = Return period of one failure in T years&lt;br /&gt;
  and  = Gumbel Parameters&lt;br /&gt;
KT = Frequency factor, obtained as:&lt;br /&gt;
&lt;br /&gt;
 							(3.12)&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
Estimation of Gumbel parameters by Method of Moments (MoM)&lt;br /&gt;
&lt;br /&gt;
Mean,  							(3.13)&lt;br /&gt;
Standard deviation,  α						(3.14)		&lt;br /&gt;
&lt;br /&gt;
The mean, μ and Standard Deviation values, σ are computed from observed annual maximum streamflow records. Note that other frequency distributions (Pearson type 3, Log-Pearson type 3, Log-Normal and General Extreme Value) have different expressions for estimating the distribution parameters.&lt;br /&gt;
&lt;br /&gt;
Step 5: Application for water permit&lt;br /&gt;
Water abstraction for water supply from a river or spring requires a permit from the respective water basin office. The planner of the water supply project must apply for the water permit abstraction early in the project design because it can affect the viability of a project. The design engineer must seek the water permit if the project involves a new, replacement, increased withdrawal from a source or an increase in the water system’s physical capacity.&lt;br /&gt;
&lt;br /&gt;
Step 6: Environmental flow considerations&lt;br /&gt;
Environmental flow may be computed in terms of magnitude, timing of low flow in the dry month, duration of low flow in days, frequency of occurrence of the low flow event (return period) and rate of change of low flow over time (m3/day of flow recession). The recommended environmental flow varies for individual rivers and streams and therefore to determine its flow value, a comprehensive Environmental Impact Assessment (EIA) should be conducted and approved by NEMC. Also, there are some guidelines and procedures for environmental flow assessment for specific catchments in Tanzania developed by NEMC. Accordingly, designers need to consult NEMC for environmental flow information in their project areas (https://www.nemc.or.tz/).&lt;br /&gt;
&lt;br /&gt;
Step 7: Data to support hydrological analysis&lt;br /&gt;
Hydrological data is invaluable for planning of water supply systems. For example, water source adequacy and reliability can be determined from analysis of streamflow data which is important hydrological data. Hydrological data expected to be collected by water basin offices in Tanzania to support the planning of water supply systems, specifically to answer questions related to the following:&lt;br /&gt;
&lt;br /&gt;
•	Water availability in terms of quantity and quality&lt;br /&gt;
•	Frequency of occurrence of low flows and flood flows&lt;br /&gt;
•	Variability of flow regime in terms of quantity and quality&lt;br /&gt;
&lt;br /&gt;
Important data to be collected include the following:&lt;br /&gt;
&lt;br /&gt;
(i)	Streamflow – required to quantify available water and estimate flood peaks and low flow magnitudes,&lt;br /&gt;
(ii)	Rainfall – required to determine 90% dependable rainfall,&lt;br /&gt;
(iii)	Sediment - Sediment deposition affects the water carrying capacity of rivers and the useful life of reservoirs. Sediment data is required to determine the useful reservoir capacity and the life span of the reservoir.&lt;br /&gt;
(iv)	 Climate data - (Evaporation, Temperature, Wind speed, sunshine hours, radiation and humidity) – required to estimate water loss from reservoirs.&lt;br /&gt;
&lt;br /&gt;
During the feasibility and preliminary design stage, the design engineer must look for streamflow records from stream gauging stations located at or near water intakes and dam sites to support the design work. In a situation where there are no gauging stations at or near water intakes or dam sites, two options may be considered to get flow data to be used in the design.&lt;br /&gt;
&lt;br /&gt;
Option 1: Transfer data from adjacent or neighbouring drainage areas that have comparable or similar characteristics. The same applies to a situation where rainfall data is missing, rainfall data from adjacent or similar catchments is used to derive flow frequency/probability curves required in the design of water supply system.&lt;br /&gt;
Option 2: Install permanent or temporary gauging stations and start recording flow data at the earliest possible time during the planning steps of the water supply project.&lt;br /&gt;
&lt;br /&gt;
3.7	Other considerations for various water sources&lt;br /&gt;
3.7.1	Water permits Considerations&lt;br /&gt;
During the course of implementation of water supply projects, designers will need to work with the relevant Water Basin Authorities and relevant catchment and sub-catchment committees to ensure all water users with water withdrawal permits are considered during the course of sizing the projects to ensure no developmental constraints are faced as a result of ignoring other users. It will be necessary to consult the updated water permits registers maintained by each Basin Water Board prior to planning expansion of any new water supply project.&lt;br /&gt;
&lt;br /&gt;
3.7.2	Conservation of water sources&lt;br /&gt;
In line with NAWAPO, the protection and conservation of water sources is one of the main duties of all the Basin Water Boards.  Intuitively, for national water resources the MoW also has the responsibility to deal with resolution of all water use conflicts. It will ensure that the WRM Act No.11 of 2009 as well as the associated regulations are fully observed by all parties. Other relevant laws such as those associated with pollution coordinated by other agencies or bodies like the National Environment Management Council (NEMC) are observed with respect to water resources. Where transboundary water resources are involved, the MoW has to ensure the protection roles that are expected of Tanzania are properly fulfilled in line with the relevant international laws, agreements or conventions stated in section 1.1.4.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
3.8	References&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=Chapter_Three:_Water_Sources_Analysis&amp;diff=521</id>
		<title>Chapter Three: Water Sources Analysis</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=Chapter_Three:_Water_Sources_Analysis&amp;diff=521"/>
		<updated>2020-03-31T11:17:13Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;Water source forms one single most important element and is a key to proper function and thus sustainability of any water supply project. Evidence shows that whenever proper water source analysis has not been adequately conducted, most of water supply projects fall into dysfunction. Thus, this chapter presents the analysis of water sources. It includes analysis of both surface and ground water. Further, the chapter gets into 'nitty gritty' of each of this category.&lt;br /&gt;
&lt;br /&gt;
=Chapter Three: Water Sources Analysis=&lt;br /&gt;
&lt;br /&gt;
==3.1	Availability of Water Resources in Tanzania Mainland==&lt;br /&gt;
Tanzania mainland is endowed with a wide range of water resources that includes the main drainage systems, river basins and natural wetlands that are identified in the next paragraphs. With respect to the drainage systems of water resources in Tanzania mainland, it is divided into five drainage systems that include:&lt;br /&gt;
* The Indian Ocean drainage system,&lt;br /&gt;
* The Internal drainage system to Lake Eyasi, Natron and Bubu depression,&lt;br /&gt;
* The Internal drainage systems to Lake Rukwa,&lt;br /&gt;
* The Atlantic Ocean drainage system through Lake Tanganyika, &lt;br /&gt;
* The Mediterranean Sea drainage system through Lake Victoria.&lt;br /&gt;
&lt;br /&gt;
The drainage systems in turn consist of nine river basins with some bearing names resembling the drainage systems. These nine basins are indicated in Figure 3.1.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
 &lt;br /&gt;
&lt;br /&gt;
Figure 3.1: The River Basins of Tanzania (Source: NWSDS, 2008)&lt;br /&gt;
&lt;br /&gt;
Legend for Figure 3.1&lt;br /&gt;
&lt;br /&gt;
(I) Pangani River Basin	(V) Lakes Nyasa Basin&lt;br /&gt;
(II) Wami/Ruvu River Basin	(VI) Internal Drainage Basin&lt;br /&gt;
(III) Rufiji River Basin	(VII) Lake Rukwa Basin&lt;br /&gt;
(IV) Ruvuma and South Coastal River Basin	(VIII) Lake Tanganyika Basin&lt;br /&gt;
(IX) Lake Victoria Basin&lt;br /&gt;
	&lt;br /&gt;
From geographical point of view, Tanzania is a party to at least eleven transboundary water resources in form of Lakes and Rivers (NWSDS, 2008). These include the following:&lt;br /&gt;
&lt;br /&gt;
* Lake Victoria,&lt;br /&gt;
* Lake Tanganyika,&lt;br /&gt;
* Lake Nyasa,&lt;br /&gt;
* Lake Chala,&lt;br /&gt;
* Lake Jipe,&lt;br /&gt;
* Kagera River,&lt;br /&gt;
* Mara River,&lt;br /&gt;
* Pangani River,&lt;br /&gt;
* Umba River,&lt;br /&gt;
* Ruvuma River and&lt;br /&gt;
* Songwe River.&lt;br /&gt;
&lt;br /&gt;
With its numerous water bodies, Tanzania is perceived to have abundant surface and groundwater resources for meeting its present consumptive and non-consumptive needs. However, the reality is that severe and widespread water shortages exist in many areas of Tanzania because of climate variability, poor distribution of the resource in terms of time and space, and inadequate management of the water resources (NWSDS, 2008). As a result, Tanzania experiences frequent and intense water shortages and some water use conflicts.&lt;br /&gt;
&lt;br /&gt;
Furthermore, Tanzania is relatively dry with more than half of the country receiving, on average, less than 800 mm of rainfall per year depending upon air circulation patterns and the movement of the convergence zones in the region. The semi-arid Central and Northern parts of the country, including areas immediately South of Lake Victoria receive less than 700 mm of rainfall per annum and are dry for an average of seven consecutive months a year. River flows in these areas are intermittent. In the Southern, Western and Northern highlands, which receive more than 1,000 mm/year of rainfall, rivers are perennial, and some of these experience frequent floods.&lt;br /&gt;
 &lt;br /&gt;
As an example, in 1999 the availability of renewable freshwater resources, both surface and groundwater was estimated  to be about 2,700 m3/capita/year. By 2018, this estimate was reduced to 2,330 m3/capita/year due to increased population alone.  The average figure is significantly above the level of 1,700 m3/capita/year set by the United Nations as denoting water stress, or 1,000 m3/capita/year denoting water scarcity. Furthermore, due to the projected population growth alone, Tanzania's annual freshwater renewal rate is projected to drop to 1,500 m3/capita/year by 2025, thus categorising the country as being water stressed by then. &lt;br /&gt;
&lt;br /&gt;
On the whole, Tanzania has sufficient surface and ground water resource potential to meet most of her present needs.  However, differences in topography, rainfall patterns and climate account for the existing variation in the availability of water in different parts of the country.  In the densely populated Pangani and Rufiji Basins, these variations have already resulted into water stress.  It is estimated that the annual surface runoff from Tanzania to the world’s oceans is about 74 x 109 m3. The Rufiji, which drains a 177,000 km2 area, contributes over 50% of the runoff3. Typical annual runoffs are shown in the Table 3.1 for some of the major rivers of Tanzania. &lt;br /&gt;
&lt;br /&gt;
Table 3.1 Mean annual river discharges for some of the principal rivers of Tanzania&lt;br /&gt;
River 	Mean Annual Discharge (Million m3/yr) &lt;br /&gt;
Rufiji (at Steiglers Gorge) 	22,250 &lt;br /&gt;
Kilombero (at Swero) 	14,470 &lt;br /&gt;
Malagarasi (at Taragi Ferry) 	5,060 &lt;br /&gt;
Ruvu (at Moro Bridge) 	1,370 &lt;br /&gt;
Wami (at Mandera) 	3,280 &lt;br /&gt;
Ruhuhu (at Kikonge) 	5,600 &lt;br /&gt;
Kiwira (at Kyela) 	1,900 &lt;br /&gt;
Kagera (at Kyaka) 	7,064 &lt;br /&gt;
Mara (at Mara Mines) 	1,971 &lt;br /&gt;
Pangani (at Hale) 	627 &lt;br /&gt;
(Source: NWSDS, 2008)&lt;br /&gt;
 &lt;br /&gt;
&lt;br /&gt;
The most abundant surface water resources exist in Lakes Victoria, Tanganyika, Nyasa, Chala and Jipe, as well as the Kagera, Mara and Songwe rivers, which are trans-boundary waters. The use of these abundant surface water resources for water supply, irrigation and other purposes is still very limited even today.&lt;br /&gt;
&lt;br /&gt;
Tanzania is also rich in wetland systems that are areas which, for part of the year, have enough water to enable the development of types of plants and animals adapted to these conditions.  These include the lakes of the Western and Eastern Rift Valley system, Lake Victoria, numerous small lakes, riverine flood plains and permanent swamps, coastal mangrove and deltaic systems, and a number of artificial impoundments and reservoirs and fish ponds.  There are numerous permanent and seasonal freshwater swamps and flood plains distributed in almost all of the country's major drainage basins, which account for some 2.7 million hectares.  The largest in this category are found in the Rufiji/Ruaha river system and in the Malagarasi/Moyowosi system, while other river systems are the Kagera River, along with Ugalla River, Suiwe River, Mara River, Pangani, Wami and Ruvu Rivers. The principal wetlands of Tanzania constitute one of the country's richest and most durable resources. &lt;br /&gt;
&lt;br /&gt;
==3.2	Water Sources Available in Tanzania Mainland==&lt;br /&gt;
In Tanzania, there are three main categories of water sources available, namely rainwater, surface and groundwater. &lt;br /&gt;
&lt;br /&gt;
===3.2.1	Rainwater and fog harvesting===&lt;br /&gt;
One of sources of water include rainwater and fog that can generate limited amounts of very clean water if they are properly collected and stored. In an area where other water sources are not available, consideration should be given to harvesting rainwater and fog.&lt;br /&gt;
&lt;br /&gt;
===3.2.2	Surface Water===&lt;br /&gt;
For design purposes, the surface water sources that can be considered include;&lt;br /&gt;
* Rivers or streams,&lt;br /&gt;
* Impoundments (Reservoirs and ponds),&lt;br /&gt;
* Springs,&lt;br /&gt;
* Lakes,&lt;br /&gt;
* Dams (charco, sand, earth etc).&lt;br /&gt;
&lt;br /&gt;
A brief description of each water source is provided below.&lt;br /&gt;
&lt;br /&gt;
3.2.2.1	 Rivers or streams &lt;br /&gt;
Rivers and streams are water sources that originate from springs located in highlands which flow down to the end of the respective drainage basin which can be lakes, seas or oceans as depicted on the map of Tanzania in Figure 3.1. &lt;br /&gt;
3.2.2.2	 Impoundments&lt;br /&gt;
Impoundments includes all types of reservoirs that emanate from road borrow pits, mining, human or natural activities that are utilised as sources of water for a formal water supply project. &lt;br /&gt;
3.2.2.3	 Springs&lt;br /&gt;
Springs include artesian or freely flowing spring water that has been tapped by an intake structure to facilitate supply of water to a designated community. Spring is a point where groundwater flows out of the ground, and is thus where the aquifer surface meets the ground surface. A spring may be ephemeral (intermittent) or perennial (continuous). Springs can be developed by enlarging the water outlet and constructing an intake structure for water catchment and storage. &lt;br /&gt;
&lt;br /&gt;
3.2.2.4	Lakes &lt;br /&gt;
Lakes found in Tanzania are either located at the end of drainage basins or are highland lakes and some of them are volcanic lakes. Tanzania is endowed with many small inland lakes apart from the third biggest lake in the world (Lake Victoria) as well as Lake Tanganyika which is the world’s deepest lake. Both lakes supply water to various localities around their respective catchments.&lt;br /&gt;
3.2.2.5	 Dams &lt;br /&gt;
Dams are classified based on the availability of construction materials. Various types of dams can be built ranging from earth fill dams, concrete dams, sand dams and charco dams. These are purposely built structures that allow impoundment of river and/or rain water for various end uses. &lt;br /&gt;
&lt;br /&gt;
3.2.3	Groundwater&lt;br /&gt;
Groundwater is that portion of rainwater which has percolated beneath the ground surface to form an underground reservoir referred to as aquifer water. The upper surface of groundwater is the water table. Groundwater is often clear, free from organic matter and bacteria due to the filtering effect of the soil on water percolating through it. However, groundwater almost always contains dissolved minerals from the soil. Groundwater is often better in terms of quality than surface waters. It is less expensive to develop for use, and usually provides more adequate supply in many areas in the country. In semi-arid and the drier parts of the country,  groundwater has played and will continue to play a major role as the sole water source for various uses especially in the central and northern parts of the country and the drier regions of Dodoma, Singida, Shinyanga, Tabora, Mwanza, Mara, Arusha, Coast and Southern Kilimanjaro.&lt;br /&gt;
&lt;br /&gt;
Groundwater can be considered as either spring water or well (or borehole) water. Springs, offer excellent water supply opportunities, but are generally found in hilly or mountainous areas only. They may require long pipelines in order to bring the water to the demand area. This is a feasible source for larger and concentrated settlements but rarely for dispersed populations. For rural water supply systems, groundwater is generally preferred as a water source. &lt;br /&gt;
&lt;br /&gt;
The main sub-types of groundwater and extraction methods are as follows:&lt;br /&gt;
&lt;br /&gt;
3.2.3.1	 Infiltration galleries/wells &lt;br /&gt;
Infiltration galleries are horizontal wells, constructed by digging a trench into the water-bearing sand and installing perforated pipes in it. Water collected in these pipes converges into a “well” from which it is pumped out. &lt;br /&gt;
3.2.3.2	 Well&lt;br /&gt;
This is a hole constructed by any method such as digging, driving, boring, or drilling for the purpose of extracting water from underground aquifers. Wells can vary greatly in depth, water volume and water quality. Well water typically contains more minerals in solution than surface water and may require treatment to soften the water by removing minerals such as arsenic, iron and manganese. Well water may be drawn by pumping from a source below the surface of the earth. Alternatively, it could be drawn up using containers, such as buckets that are raised mechanically or by hand.&lt;br /&gt;
&lt;br /&gt;
Wells are various types of artificially constructed water production wells that are designated as shallow wells (up to 20 metres deep) or deep wells (more than 20 metres deep) as designated by the Ministry responsible for water from time to time.  Water is pumped out of the well into the end user containers or a storage tank using various types of pumps that can be driven manually or using various energies. Typical cross sections through such wells are given in Section 3.6.5.&lt;br /&gt;
3.2.3.3	Classification of wells based on the aquifer tapped&lt;br /&gt;
As mentioned, an aquifer contains a considerable amount of groundwater underground beneath layers of permeable soil material like sand or gravel. Aside from their water storage capacity, aquifers allow the underground flow of groundwater. Aquifers are recharged with rainwater that seeps down to the soil and through the permeable layers.&lt;br /&gt;
3.2.3.3.1	Shallow wells&lt;br /&gt;
Generally, a well is considered shallow if it is less than 20 metres deep. Shallow wells tap the upper water-bearing layer underground. This permeable layer, however, usually has limited safe yield due to its great dependence on seasonal rainfalls. Therefore, the supply capacity of shallow wells could be unreliable and are sometimes intermittent. Also, the water extracted from the upper strata is usually more affected by contamination since the aquifer being tapped is near the ground surface where possible sources of contamination are abound. Protection against contamination is therefore one of the main considerations in constructing a shallow well.&lt;br /&gt;
3.2.3.3.2	Deep wells&lt;br /&gt;
Deep wells, which are over 20 metres deep, tap the deeper unconfined aquifer. This aquifer is not confined by an overlying impermeable layer and is characterized by the presence of a water table. A deep well is less susceptible to surface contamination because of the deeper aquifer. Also, its yield tends to be more reliable since it is less affected by seasonal precipitation.&lt;br /&gt;
&lt;br /&gt;
3.2.3.3.3	Artesian wells&lt;br /&gt;
Artesian wells are much like the deep wells except that the water extracted is from a confined aquifer. The confining impermeable layers are above and below the aquifer. Groundwater recharge enters the aquifer through permeable layers at high elevations causing the confined groundwater at the lower elevations to be under pressure. In some cases, the hydraulic pressure of the aquifer is sufficient for a well to flow freely at the well head.&lt;br /&gt;
&lt;br /&gt;
3.3	Quality Suitability of Water Sources for Water Supply Projects&lt;br /&gt;
When considering the different water sources for water supply projects, it is necessary to ensure that the quality of the water source expected to be utilised is monitored well preferably for a period of not less than three years consecutively to ensure the variability of the quality is captured during the wet and dry seasons. When one looks at the list of the potential sources presented in the foregoing section, such a monitoring programme may not be necessary for rainwater and fog. Only short-term monitoring of the quality of these two sources should be undertaken.&lt;br /&gt;
&lt;br /&gt;
3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment&lt;br /&gt;
&lt;br /&gt;
A decision on whether the water source needs to be subject to water treatment or otherwise will emanate from the results of the short term tests on the quality of the water which will in turn guide the decision of pilot testing the recommended flow sheets particularly for river/streams, lakes, impoundments and dams. Groundwater will usually need only a few unit operations for removal of the identified elevated impurities that may include Iron, Manganese or Fluoride and the need to disinfect water from shallow wells in addition to maintaining residual disinfectants for prevention of re-contamination. Rainwater and condensates from fog will not need to be pilot tested.&lt;br /&gt;
&lt;br /&gt;
3.5	General Considerations for Selection of Water Sources &lt;br /&gt;
In the selection of a source or sources of water supply, adequacy and reliability of the available supply can be considered as the overriding criteria. Without these, the water supply system cannot be considered viable. These, together with the other factors that should be considered (and which are interdependent), are as follows:&lt;br /&gt;
&lt;br /&gt;
3.5.1	Adequacy and reliability&lt;br /&gt;
Adequacy of water supply requires that the quantity of water flow of water source be large enough to meet present and future water demand. On the other hand, source reliability can be expressed by how frequently a water system expects normal demand to go unmet, such as a one-in -25 year or even a one-in-50 year drought. Safe yield is a 1-day low flow rate that is exceeded for 96 percent of the period of record and that can be related to the determined average daily water demand in order to establish the reliability of a water source. For a river/stream, safe yield represents the minimum flow rate that will guarantee no risk to the river hydrology and its surroundings. Safe yield is estimated so as to check whether the planned withdrawal for water supply purposes will be met. To determine the safe yield of a river or stream, a flow -frequency/probability analysis presented in section 3.1.5.5 should be performed. From the analysis, the determined 96 % low flow index should be taken as the safe yield of the river or stream and thus considered as the water source reliability.&lt;br /&gt;
&lt;br /&gt;
3.5.2	Quality of water sources&lt;br /&gt;
The assessment of water quality of a water source is important to establish the suitability of water source for human consumption. The quality of surface water is determined by the amount of pollutants and contaminants picked up by the water in the course of its travel. While flowing over the ground, surface water collects silt, decaying organic matter, bacteria and other micro-organisms from the soil. Sources which require little or no treatment of the water should be chosen in the first instance, provided the required quantity of water can be obtained. Hence springs and ground water resources should always be exploited in the first hand. Surface water from rivers, streams and lakes will almost always require some treatment to render it safe for human consumption. However, for large supplies, surface water will often still be the most economical alternative. Rivers which have the bulk of their catchments in forest areas should be preferred.&lt;br /&gt;
&lt;br /&gt;
Thus, all surface water sources should be presumed to be unsafe for human consumption without some form of treatment. The option to treat surface water to make it safe for human consumption in compliance with the latest edition of Tanzania potable water standards (TBS, TZS 789) has to be evaluated to decide on the feasibility of the water supply project.&lt;br /&gt;
&lt;br /&gt;
3.5.3	Technical Requirements&lt;br /&gt;
The development of the source should be technically feasible, the operation and maintenance requirements for the source abstraction and supply system should be appropriate to the resources available.&lt;br /&gt;
&lt;br /&gt;
3.5.4	Cost implications to develop a water source&lt;br /&gt;
The assessment of investment costs to develop a given water source including operation and maintenance costs has a bearing in the selection of the water source for development. Affordability of investment costs is an important factor to be considered in the selection of the water source.&lt;br /&gt;
&lt;br /&gt;
3.5.5	Protection of water sources&lt;br /&gt;
The location of a water source is a key factor in securing the highest quality water source. In analysing a source location, the design engineer should consider the measures necessary to protect the water source from human excreta, from industrial discharges and from agricultural run-off. In addition, measures to establish and maintain watershed control, physical protection and barriers to contamination have to be considered to ensure sustainable quantity and quality of the raw water.&lt;br /&gt;
&lt;br /&gt;
3.5.6	Legal and management requirements&lt;br /&gt;
Ownership of the land and the legal requirements of obtaining permission to abstract are also factors to consider when selecting a source. Sources on private land may cause access problems.&lt;br /&gt;
&lt;br /&gt;
3.5.7	Distance of water supply source&lt;br /&gt;
The source of the water supply must be situated as near to the demand area as possible. Hence, less length of pipes needs to be installed and thus economical transfer and supply of water. The source(s) nearest to the demand area is usually selected.&lt;br /&gt;
&lt;br /&gt;
3.5.8	Topography of the project area and its surroundings&lt;br /&gt;
The area or land between the source and the area to be served by water supply system should not be highly uneven, i.e., it should not have steep slopes because cost of construction or laying of pipes is very high in such areas.&lt;br /&gt;
&lt;br /&gt;
3.5.9	Elevation of a source of water supply&lt;br /&gt;
The source of water must be on a high elevation than the demand area so as to provide sufficient residual pressure in the water for daily requirements. When the water is available at lower levels, then pumps are used to pressurize water. This requires an excess developmental and operational tasks and costs.&lt;br /&gt;
&lt;br /&gt;
3.6	Determination of water source yield&lt;br /&gt;
Sources which require little or no treatment of raw water such as springs, wells and boreholes should be given the highest selection priority provided their yields are sufficient to meet the water demands of the water supply scheme. For large supplies, surface water will continue to be the most economical alternative water source. In selecting surface water sources, rivers with upland and mostly forested catchments should be given preference. Sub-surface water drawn from a riverbed or river bank can sometimes be a viable alternative in dry areas with only seasonal flows in the river, or in rivers with a high silt load.&lt;br /&gt;
&lt;br /&gt;
Sources from which water can be supplied by a gravity system are particularly more favourable than those which require pumping with significant energy costs. For household and small community water supplies, rainwater harvesting will be the most appropriate in most medium and high potential areas in Tanzania that receive sufficient rains.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
3.6.1	Rainwater and fog harvesting&lt;br /&gt;
3.6.1.1	 Rainwater harvesting&lt;br /&gt;
Rainwater harvesting is a technique of collection and storage of rainwater into natural reservoirs or tanks, or the infiltration of surface water into subsurface aquifers (before it is lost as surface runoff). Types of rainwater harvesting systems are described in the sections below.&lt;br /&gt;
&lt;br /&gt;
3.6.1.1.1	Types of rainwater harvesting&lt;br /&gt;
Two types of rainwater harvesting should be considered:&lt;br /&gt;
&lt;br /&gt;
•	Land catchment,&lt;br /&gt;
•	Roof catchment.&lt;br /&gt;
&lt;br /&gt;
Important data for design of rainwater harvesting systems:&lt;br /&gt;
•	Rainfall data&lt;br /&gt;
•	Catchment/Surface Area &lt;br /&gt;
•	Run-off Coefficient&lt;br /&gt;
&lt;br /&gt;
To accurately estimate the potential rainwater supply from a catchment, reliable rainfall data for a 10-year period is required . The Hydrology Section, Tanzania Meteorology Agency, and Agriculture Departments should be contacted for rainfall data wherever rainwater-harvesting technology is proposed. &lt;br /&gt;
&lt;br /&gt;
The amount of rainfall collected depends on the surfaces where rain falls and the runoff coefficient K of the surface. The runoff coefficient varies with topography, land use, vegetation cover, soil type and moisture content of the soil. In selecting run off coefficients the future characteristics of the water shed are considered. If land use varies within a water shed consider the segments individually and use a weighted coefficient value to determine the total runoff for the watershed. Practically annual rainfall falls during the rainy seasons between October and May.&lt;br /&gt;
&lt;br /&gt;
(i) Run-off Coefficients&lt;br /&gt;
Table 3:2 shows the runoff coefficients for various surfaces. They should be used for calculating the fraction of the rainfall which can be harvested.&lt;br /&gt;
&lt;br /&gt;
Table 3.2: Run-Off Coefficients for Different Surfaces&lt;br /&gt;
SURFACE	RUN-OFF&lt;br /&gt;
COEFFICIENT (K)&lt;br /&gt;
1.	Roof catchments	&lt;br /&gt;
	•	Roof tiles	0.8 to 0.9&lt;br /&gt;
	•	Corrugated sheets	0.7 to 0.9&lt;br /&gt;
2.	Ground surface covering&lt;br /&gt;
	•	Concreted	0.6 to 0.8&lt;br /&gt;
	•	Bitumen, plastic sheeting, butyl rubber	0.8 to 0.9&lt;br /&gt;
	•	Pavement of stone, bricks with open joints	0.5 to 0.6&lt;br /&gt;
	•	Pavement of stone, bricks with tightly cemented joints	0.75-0.85&lt;br /&gt;
3.	Compacted and smoothened soil	0.3 to 0.5&lt;br /&gt;
4. Lawns, sandy soil&lt;br /&gt;
	•	2% slope	0.05-0.10&lt;br /&gt;
	•	2.7% slope	0.10-0.15&lt;br /&gt;
	•	&amp;gt;7%	0.15-0.20&lt;br /&gt;
5. Lawns, heavy soil&lt;br /&gt;
	•	2% Slope	0.13-0.17&lt;br /&gt;
	•	2.7% slope	0.18-0.22&lt;br /&gt;
	•	&amp;gt;7%	0.25-0.35&lt;br /&gt;
6.	•	Uncovered surface, flat terrain	0.3&lt;br /&gt;
	•	Uncovered surface, slope less than 10%	0.0 to 0.4&lt;br /&gt;
	•	Rocky natural catchments	0.2 to 0.5&lt;br /&gt;
&lt;br /&gt;
3.6.1.1.2	Components of rainwater harvesting system&lt;br /&gt;
a) Catchments Area: The catchment of a water harvesting system is the surface which directly receives the rainfall and provides water to the system.&lt;br /&gt;
b) Coarse mesh at the roof to prevent the passage of debris.&lt;br /&gt;
c) Gutters to collect and transport rainwater to the storage tank. Gutters can be semi-circular or rectangular and could be made using:&lt;br /&gt;
&lt;br /&gt;
•	Locally available material such as plain galvanised iron sheet (20 to 22 gauge), folded to required shapes &lt;br /&gt;
•	Semi-circular gutters of PVC material can be readily prepared by cutting those pipes into two equal semi-circular channels.&lt;br /&gt;
•	Bamboo trunks cut vertically in half&lt;br /&gt;
&lt;br /&gt;
The size of the gutter should be according to the flow during the highest intensity rain. It is advisable to make them 10 to 15 per cent oversize.&lt;br /&gt;
&lt;br /&gt;
d) Conduits/pipeline that carry rainwater from the catchment or rooftop area to the harvesting system. Conduits can be of any material like polyvinyl chloride (PVC) or galvanized iron (GI), materials that are commonly available.&lt;br /&gt;
&lt;br /&gt;
e) First Flush pipe to separate first rainwater contaminants namely debris, dirt, and dust.&lt;br /&gt;
&lt;br /&gt;
3.6.1.1.3	Estimation of the yield&lt;br /&gt;
A first estimate of the average yield of a catchments area can be found using the following expression.&lt;br /&gt;
S = K × I × A						(3.1)&lt;br /&gt;
Where: &lt;br /&gt;
S = Yield in m3 / annum &lt;br /&gt;
A = Area of catchment/surface, m2 &lt;br /&gt;
I = Average annual rainfall m/annum &lt;br /&gt;
K = runoff coefficient &lt;br /&gt;
&lt;br /&gt;
Determination of average runoff coefficient for the entire catchment area composed of different surfaces can be calculated as follows:&lt;br /&gt;
 +...					(3.2)&lt;br /&gt;
The required capacity of the collection facility should be calculated using available meteorological data showing the rainfall pattern of the area. However, for rough calculations the storage tank, capacity may be calculated as follows:&lt;br /&gt;
C = D × T × 10-3						(3.3)&lt;br /&gt;
&lt;br /&gt;
Where:&lt;br /&gt;
C = Capacity of tank in m3 &lt;br /&gt;
D = Total water demand in litres / day&lt;br /&gt;
T = Longest dry spell in days&lt;br /&gt;
&lt;br /&gt;
3.6.2	Hydrological Analysis of Surface Waters&lt;br /&gt;
The Design Manual for Water Supply projects is expected to reflect the best concepts on what constitutes the basis for designing a safe, reliable and sustainable water system. Hydrological principles must be taken into consideration during the feasibility and preliminary design stages of the water supply system to ensure that from the outset, design and construction of the system is done right. The design engineer must apply hydrological principles during design of the water system to ensure that the system being designed does not result in exhausted water supply sources and empty reservoirs after construction of the project is completed. If it is recognised from the beginning that there is water deficiency from the source, then the water source should not be considered for development.&lt;br /&gt;
&lt;br /&gt;
The following steps should be followed when undertaking hydrological analysis for the water supply projects:&lt;br /&gt;
&lt;br /&gt;
Step 1: Measurement of the quantity of surface water sources,&lt;br /&gt;
Step 2: Low flow assessment of surface water sources,&lt;br /&gt;
Step 3: Flood flow estimation,&lt;br /&gt;
Step 4: Rainfall analysis,&lt;br /&gt;
Step 5: Water permit application,&lt;br /&gt;
Step 6: Data to support hydrological analysis.&lt;br /&gt;
&lt;br /&gt;
Step 1: Measurement of River Discharge&lt;br /&gt;
In order to assess the amount of water available from the identified surface water source, a discharge measurement must be carried out during both the dry and wet seasons. Measurement of discharge will highlight the production capacity of a water source, the information which is important in the planning of a water system. An estimate of the quantity of water that can be reliably produced by a water source gives the planner a basis to decide for or against its development. For the sources to be considered adequate, they must at least satisfy the average day water demand of the area to be served by a water system. The average daily water demand is calculated from estimated average water requirements for domestic, commercial, industrial, public institutions and livestock. The following methods can be used to measure discharge.&lt;br /&gt;
&lt;br /&gt;
a) Volumetric Method&lt;br /&gt;
This method is appropriate for measuring small quantities of flow from small streams and springs. Flow can be measured by measuring the volume. The equipment required are a stop watch and a bucket or drum of known volume. The method consists of determining the time required to fill the bucket or drum. For more accurate results, the measurement is repeated several times, and the average time of these trials is taken.&lt;br /&gt;
&lt;br /&gt;
b) V-Notch Weir Method&lt;br /&gt;
A weir is an overflow structure built across an open channel for the purpose of measuring the rate of flow. Weirs may be rectangular, trapezoidal or triangular in shape. The triangular or V-Notch Weir is a flow measuring device particularly suited for small flows. The V-Notch Weir often used in flow measurements is the 90° V-Notch that is placed in the middle of the channel and water is allowed to flow over it. The water level in the channel is then measured using a gauging rod. The zero point in the rod should be level with the sill or crest of weir/notch. For a known height of water above the zero in the rod, the flow in cumecs for the 90° V-Notch can be obtained by using the formula:&lt;br /&gt;
&lt;br /&gt;
 							(3.4)&lt;br /&gt;
&lt;br /&gt;
 								(3.5)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
Q = Discharge in m3/sec&lt;br /&gt;
H =Height of Water level above the crest of the weir in meters&lt;br /&gt;
In this case, the discharge coefficient of the weir is approximated to be equal to 0.58.&lt;br /&gt;
&lt;br /&gt;
c) Current meter Measurement&lt;br /&gt;
The current meter is an instrument that is used to measure relatively larger quantities of flow from streams and rivers. The instrument consists of a propeller rotating freely on a well-lubricated shaft. The device is lowered into the water and the rate of revolution of the impeller is directly proportional to the velocity of the water flow. A small magnet is usually built into the shaft of the instrument and a coil detects the passage of the magnet and allows the number of revolutions of the shaft in the given time to be counted. Once the rate of revolution of the impeller is known the water velocity can be calculated using the calibration equation for the instrument, which is expressed as follows:&lt;br /&gt;
&lt;br /&gt;
 									(3.6)&lt;br /&gt;
&lt;br /&gt;
Where, &lt;br /&gt;
V is the water velocity in meters per second&lt;br /&gt;
n is the number of revolutions of the impeller per second&lt;br /&gt;
a, b are constants for the particular instrument.&lt;br /&gt;
&lt;br /&gt;
The discharge measurement using the current meter at the time of measurement, Q,  is  determined by multiplying the velocity of flow and water flow cross-section area.&lt;br /&gt;
&lt;br /&gt;
Step 2: Low flow assessment&lt;br /&gt;
The assessment of low flow magnitudes of streams/rivers or springs in hydrology is important in the planning of a water supply system in view of the fact that it reflects on the water source adequacy and reliability to meet the consumer demand. In low flow hydrology, two questions are asked about a particular river identified to be a water source for a given water supply system:&lt;br /&gt;
&lt;br /&gt;
(i)	Does the river supply a particular water demand at all times?&lt;br /&gt;
(ii)	If not, how much water must be stored in order to meet any deficiency which may arise?&lt;br /&gt;
&lt;br /&gt;
Techniques of flow duration curves, annual minimum flow analyses and annual drought volumes are applied to address the two questions.&lt;br /&gt;
&lt;br /&gt;
a) Flow duration curve&lt;br /&gt;
The flow-duration curve (FDC) is defined as a cumulative frequency curve that shows the percent of time specified discharges were equalled or exceeded during a given period. It combines in one curve the flow characteristics of a stream throughout the range of discharge, without regard to the sequence of occurrence. To prepare a flow-duration curve, the daily, weekly, or monthly flows during a given period are arranged according to magnitude, and then percent of time during which specified flow values are equalled or exceeded are computed. &lt;br /&gt;
&lt;br /&gt;
A flow duration curve once it is prepared, is used to determine the indices of low flow magnitudes; for example, the 96-percentile flow (Q96), is the flow that is exceeded for 96 percent of the period of record. This discharge value is a useful index of low flow that is related to the quantity of water that can be available for water supply in the dry season.&lt;br /&gt;
&lt;br /&gt;
The following steps are followed to construct the FDC:&lt;br /&gt;
&lt;br /&gt;
(i)	Rank the observed stream flows in descending order (from the maximum to the minimum value).&lt;br /&gt;
(ii)	Calculate exceedance probability (P) of each flow as follows:&lt;br /&gt;
&lt;br /&gt;
		 						(3.7)&lt;br /&gt;
&lt;br /&gt;
		Where,&lt;br /&gt;
			P is the probability that a given flow will be equalled or exceeded 			(% of time),&lt;br /&gt;
			m is the ranked position of a given flow value on the list,&lt;br /&gt;
			n is the length of the sample.&lt;br /&gt;
&lt;br /&gt;
(iii)	 A FDC is obtained by plotting each ordered observed streamflow value versus the corresponding calculated exceedance probability.&lt;br /&gt;
(iv)	 Read the indices of low flow magnitudes from the FDC corresponding to 90%, 95% and 99% probabilities of exceeded.&lt;br /&gt;
&lt;br /&gt;
b) Low flow frequency analysis&lt;br /&gt;
The frequency analysis of low river flows is performed by analyzing 1-day or 7-day or 10-day annual minimum flow series obtained by selecting the lowest flow values occurring in each year of record. The set of observed annual minimum flow values recorded at any gauging station is assumed to be a random statistical sample from the population of all possible annual minima at the given site.&lt;br /&gt;
&lt;br /&gt;
The selected set of observed annual minimum flow values is fitted to the Gumbel statistical distribution and then the annual minimum flow magnitudes (QT) corresponding to the design probability of failure (1/T) is then estimated from the Gumbel prediction equation:&lt;br /&gt;
&lt;br /&gt;
 								(3.8)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
QT = Low flow magnitude&lt;br /&gt;
T = Return period of one failure in T years&lt;br /&gt;
  and  = Gumbel Parameters &lt;br /&gt;
KT = Frequency factor, obtained as:&lt;br /&gt;
&lt;br /&gt;
 							       (3.9)&lt;br /&gt;
&lt;br /&gt;
Results from low flow frequency analysis:&lt;br /&gt;
(i)	If the value of QT is large in comparison to QD, the average day water demand, then the river can be considered to be able to supply the demand satisfactorily.&lt;br /&gt;
(ii)	On the other hand if QT is less than or of the same order of magnitude as, QD, ,then the river alone without some form of flow regulation could not be considered satisfactory for supplying the demand. &lt;br /&gt;
&lt;br /&gt;
c) Annual drought volumes Analysis&lt;br /&gt;
On the basis of the results obtained from low flow frequency analysis, in case the annual minimum flow magnitudes (QT) corresponding to the design probability of failure (1/T) is found to be less than QD, demand flow, then storage will be required to meet the established water demand. The required storage is determined by carrying out deficiency/drought Volumes Analysis.&lt;br /&gt;
&lt;br /&gt;
The storage required on a river to meet a specific demand depends on the following factors:&lt;br /&gt;
&lt;br /&gt;
•	Variability of the river flow&lt;br /&gt;
•	Magnitude of the demand&lt;br /&gt;
•	Degree of reliability of meeting the demand&lt;br /&gt;
&lt;br /&gt;
The capacity of the reservoir required to augment the river flow in any year can  be determined from the analysis of the series of annual maximum deficiencies (drought volumes) as follows:&lt;br /&gt;
&lt;br /&gt;
Drought volumes V1, V2, V3,…, Vn are computed from a hydrometric record of the river flow (Qi), with reference to the demand flow (QD), i.e., (Vi = Qi-QD). &lt;br /&gt;
&lt;br /&gt;
The set of observed annual maximum deficiencies at any gauging station is assumed to be a random statistical sample. The annual maximum deficiency (VT) corresponding to the probability of failure (1/T) is estimated from the series of annual maximum deficiencies using a statistical distribution, e.g., Gumbel distribution as illustrated in previous section. The design storage of the reservoir can be made equal to the volume VT corresponding to a risk of one failure in T years. &lt;br /&gt;
&lt;br /&gt;
Step 3: Dependable Rainfall Analysis&lt;br /&gt;
Rainfall analysis is carried out when the need arises to determine dependable rainfall in a given area for the purpose of designing a rainwater harvesting system for domestic use. Frequency analysis of recorded annual rainfall data from a given area, enables the determination of the 90% dependable annual rainfall. This is the value of rainfall magnitude that will be exceeded 90% of the time. In the design of Rainwater Water Harvesting system, catchment (i.e. roof) area and depth of rainfall are important parameters for estimation of optimal storage size. Taking note of the fact that rainfall amounts vary on a year to year basis, the computed rainfall magnitude that is exceeded 90% of the time, is taken as the value of annual rainfall depth that can be expected to occur with some degree of certainty and thus used in the design. The exceedance probability is determined by ranking the observed annual rainfall in ascending order (from the minimum to the maximum value) and then calculating non-exceedance probability (P) as follows:&lt;br /&gt;
&lt;br /&gt;
 								(3.10)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
P is the probability that a given rainfall will be equalled or not exceeded (% of time),&lt;br /&gt;
m is the ranked position of a given rainfall value on the list,&lt;br /&gt;
n is the length of the sample.&lt;br /&gt;
&lt;br /&gt;
The probability of dependable rainfall is obtained by calculating  the value of exceedance probability (1 – P).&lt;br /&gt;
&lt;br /&gt;
Step 4: Flood flow estimation for intakes and small dams' spillways&lt;br /&gt;
The need to estimate flood peaks or design floods arises where it is required to design a spillway of a dam proposed for water storage and also the design of water intake structures. Water intakes and spillway of small dams are designed to accommodate the 100-year flood. &lt;br /&gt;
&lt;br /&gt;
Frequency analysis of observed Annual Maximum streamflow records from a gauging station enables the estimation of flood peaks. The statistical distribution namely the Gumbel distribution or other statistical distribution used in Tanzania such as Pearson type 3, Log-Pearson type 3, Log-Normal and General Extreme Value can be used to carry out frequency analysis in order to determine the magnitude of flood peak of 100-year required for the design. The estimation of design flood peak magnitudes for specified return periods using the Gumbel Distribution is illustrated below.&lt;br /&gt;
&lt;br /&gt;
Prediction equation&lt;br /&gt;
&lt;br /&gt;
 								(3.11)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
QT = Flood peak magnitude&lt;br /&gt;
T = Return period of one failure in T years&lt;br /&gt;
  and  = Gumbel Parameters&lt;br /&gt;
KT = Frequency factor, obtained as:&lt;br /&gt;
&lt;br /&gt;
 							(3.12)&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
Estimation of Gumbel parameters by Method of Moments (MoM)&lt;br /&gt;
&lt;br /&gt;
Mean,  							(3.13)&lt;br /&gt;
Standard deviation,  α						(3.14)		&lt;br /&gt;
&lt;br /&gt;
The mean, μ and Standard Deviation values, σ are computed from observed annual maximum streamflow records. Note that other frequency distributions (Pearson type 3, Log-Pearson type 3, Log-Normal and General Extreme Value) have different expressions for estimating the distribution parameters.&lt;br /&gt;
&lt;br /&gt;
Step 5: Application for water permit&lt;br /&gt;
Water abstraction for water supply from a river or spring requires a permit from the respective water basin office. The planner of the water supply project must apply for the water permit abstraction early in the project design because it can affect the viability of a project. The design engineer must seek the water permit if the project involves a new, replacement, increased withdrawal from a source or an increase in the water system’s physical capacity.&lt;br /&gt;
&lt;br /&gt;
Step 6: Environmental flow considerations&lt;br /&gt;
Environmental flow may be computed in terms of magnitude, timing of low flow in the dry month, duration of low flow in days, frequency of occurrence of the low flow event (return period) and rate of change of low flow over time (m3/day of flow recession). The recommended environmental flow varies for individual rivers and streams and therefore to determine its flow value, a comprehensive Environmental Impact Assessment (EIA) should be conducted and approved by NEMC. Also, there are some guidelines and procedures for environmental flow assessment for specific catchments in Tanzania developed by NEMC. Accordingly, designers need to consult NEMC for environmental flow information in their project areas (https://www.nemc.or.tz/).&lt;br /&gt;
&lt;br /&gt;
Step 7: Data to support hydrological analysis&lt;br /&gt;
Hydrological data is invaluable for planning of water supply systems. For example, water source adequacy and reliability can be determined from analysis of streamflow data which is important hydrological data. Hydrological data expected to be collected by water basin offices in Tanzania to support the planning of water supply systems, specifically to answer questions related to the following:&lt;br /&gt;
&lt;br /&gt;
•	Water availability in terms of quantity and quality&lt;br /&gt;
•	Frequency of occurrence of low flows and flood flows&lt;br /&gt;
•	Variability of flow regime in terms of quantity and quality&lt;br /&gt;
&lt;br /&gt;
Important data to be collected include the following:&lt;br /&gt;
&lt;br /&gt;
(i)	Streamflow – required to quantify available water and estimate flood peaks and low flow magnitudes,&lt;br /&gt;
(ii)	Rainfall – required to determine 90% dependable rainfall,&lt;br /&gt;
(iii)	Sediment - Sediment deposition affects the water carrying capacity of rivers and the useful life of reservoirs. Sediment data is required to determine the useful reservoir capacity and the life span of the reservoir.&lt;br /&gt;
(iv)	 Climate data - (Evaporation, Temperature, Wind speed, sunshine hours, radiation and humidity) – required to estimate water loss from reservoirs.&lt;br /&gt;
&lt;br /&gt;
During the feasibility and preliminary design stage, the design engineer must look for streamflow records from stream gauging stations located at or near water intakes and dam sites to support the design work. In a situation where there are no gauging stations at or near water intakes or dam sites, two options may be considered to get flow data to be used in the design.&lt;br /&gt;
&lt;br /&gt;
Option 1: Transfer data from adjacent or neighbouring drainage areas that have comparable or similar characteristics. The same applies to a situation where rainfall data is missing, rainfall data from adjacent or similar catchments is used to derive flow frequency/probability curves required in the design of water supply system.&lt;br /&gt;
Option 2: Install permanent or temporary gauging stations and start recording flow data at the earliest possible time during the planning steps of the water supply project.&lt;br /&gt;
&lt;br /&gt;
3.7	Other considerations for various water sources&lt;br /&gt;
3.7.1	Water permits Considerations&lt;br /&gt;
During the course of implementation of water supply projects, designers will need to work with the relevant Water Basin Authorities and relevant catchment and sub-catchment committees to ensure all water users with water withdrawal permits are considered during the course of sizing the projects to ensure no developmental constraints are faced as a result of ignoring other users. It will be necessary to consult the updated water permits registers maintained by each Basin Water Board prior to planning expansion of any new water supply project.&lt;br /&gt;
&lt;br /&gt;
3.7.2	Conservation of water sources&lt;br /&gt;
In line with NAWAPO, the protection and conservation of water sources is one of the main duties of all the Basin Water Boards.  Intuitively, for national water resources the MoW also has the responsibility to deal with resolution of all water use conflicts. It will ensure that the WRM Act No.11 of 2009 as well as the associated regulations are fully observed by all parties. Other relevant laws such as those associated with pollution coordinated by other agencies or bodies like the National Environment Management Council (NEMC) are observed with respect to water resources. Where transboundary water resources are involved, the MoW has to ensure the protection roles that are expected of Tanzania are properly fulfilled in line with the relevant international laws, agreements or conventions stated in section 1.1.4.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
3.8	References&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=Chapter_Three:_Water_Sources_Analysis&amp;diff=520</id>
		<title>Chapter Three: Water Sources Analysis</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=Chapter_Three:_Water_Sources_Analysis&amp;diff=520"/>
		<updated>2020-03-31T11:04:41Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;Water source forms one single most important element and is a key to proper function and thus sustainability of any water supply project. Evidence shows that whenever proper water source analysis has not been adequately conducted, most of water supply projects fall into dysfunction. Thus, this chapter presents the analysis of water sources. It includes analysis of both surface and ground water. Further, the chapter gets into 'nitty gritty' of each of this category.&lt;br /&gt;
&lt;br /&gt;
=Chapter Three: Water Sources Analysis=&lt;br /&gt;
&lt;br /&gt;
==3.1	Availability of Water Resources in Tanzania Mainland==&lt;br /&gt;
Tanzania mainland is endowed with a wide range of water resources that includes the main drainage systems, river basins and natural wetlands that are identified in the next paragraphs. With respect to the drainage systems of water resources in Tanzania mainland, it is divided into five drainage systems that include:&lt;br /&gt;
* The Indian Ocean drainage system,&lt;br /&gt;
* The Internal drainage system to Lake Eyasi, Natron and Bubu depression,&lt;br /&gt;
* The Internal drainage systems to Lake Rukwa,&lt;br /&gt;
* The Atlantic Ocean drainage system through Lake Tanganyika, &lt;br /&gt;
* The Mediterranean Sea drainage system through Lake Victoria.&lt;br /&gt;
&lt;br /&gt;
The drainage systems in turn consist of nine river basins with some bearing names resembling the drainage systems. These nine basins are indicated in Figure 3.1.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
 &lt;br /&gt;
&lt;br /&gt;
Figure 3.1: The River Basins of Tanzania (Source: NWSDS, 2008)&lt;br /&gt;
&lt;br /&gt;
Legend for Figure 3.1&lt;br /&gt;
&lt;br /&gt;
(I) Pangani River Basin	(V) Lakes Nyasa Basin&lt;br /&gt;
(II) Wami/Ruvu River Basin	(VI) Internal Drainage Basin&lt;br /&gt;
(III) Rufiji River Basin	(VII) Lake Rukwa Basin&lt;br /&gt;
(IV) Ruvuma and South Coastal River Basin	(VIII) Lake Tanganyika Basin&lt;br /&gt;
(IX) Lake Victoria Basin&lt;br /&gt;
	&lt;br /&gt;
From geographical point of view, Tanzania is a party to at least eleven transboundary water resources in form of Lakes and Rivers (NWSDS, 2008). These include the following:&lt;br /&gt;
&lt;br /&gt;
•	Lake Victoria,&lt;br /&gt;
•	Lake Tanganyika,&lt;br /&gt;
•	Lake Nyasa,&lt;br /&gt;
•	Lake Chala,&lt;br /&gt;
•	Lake Jipe,&lt;br /&gt;
•	Kagera River,&lt;br /&gt;
•	Mara River,&lt;br /&gt;
•	Pangani River,&lt;br /&gt;
•	Umba River,&lt;br /&gt;
•	Ruvuma River and&lt;br /&gt;
•	Songwe River.&lt;br /&gt;
&lt;br /&gt;
With its numerous water bodies, Tanzania is perceived to have abundant surface and groundwater resources for meeting its present consumptive and non-consumptive needs. However, the reality is that severe and widespread water shortages exist in many areas of Tanzania because of climate variability, poor distribution of the resource in terms of time and space, and inadequate management of the water resources (NWSDS, 2008). As a result, Tanzania experiences frequent and intense water shortages and some water use conflicts.&lt;br /&gt;
&lt;br /&gt;
Furthermore, Tanzania is relatively dry with more than half of the country receiving, on average, less than 800 mm of rainfall per year depending upon air circulation patterns and the movement of the convergence zones in the region. The semi-arid Central and Northern parts of the country, including areas immediately South of Lake Victoria receive less than 700 mm of rainfall per annum and are dry for an average of seven consecutive months a year. River flows in these areas are intermittent. In the Southern, Western and Northern highlands, which receive more than 1,000 mm/year of rainfall, rivers are perennial, and some of these experience frequent floods.&lt;br /&gt;
 &lt;br /&gt;
As an example, in 1999 the availability of renewable freshwater resources, both surface and groundwater was estimated  to be about 2,700 m3/capita/year. By 2018, this estimate was reduced to 2,330 m3/capita/year due to increased population alone.  The average figure is significantly above the level of 1,700 m3/capita/year set by the United Nations as denoting water stress, or 1,000 m3/capita/year denoting water scarcity. Furthermore, due to the projected population growth alone, Tanzania's annual freshwater renewal rate is projected to drop to 1,500 m3/capita/year by 2025, thus categorising the country as being water stressed by then. &lt;br /&gt;
&lt;br /&gt;
On the whole, Tanzania has sufficient surface and ground water resource potential to meet most of her present needs.  However, differences in topography, rainfall patterns and climate account for the existing variation in the availability of water in different parts of the country.  In the densely populated Pangani and Rufiji Basins, these variations have already resulted into water stress.  It is estimated that the annual surface runoff from Tanzania to the world’s oceans is about 74 x 109 m3. The Rufiji, which drains a 177,000 km2 area, contributes over 50% of the runoff3. Typical annual runoffs are shown in the Table 3.1 for some of the major rivers of Tanzania. &lt;br /&gt;
&lt;br /&gt;
Table 3.1 Mean annual river discharges for some of the principal rivers of Tanzania&lt;br /&gt;
River 	Mean Annual Discharge (Million m3/yr) &lt;br /&gt;
Rufiji (at Steiglers Gorge) 	22,250 &lt;br /&gt;
Kilombero (at Swero) 	14,470 &lt;br /&gt;
Malagarasi (at Taragi Ferry) 	5,060 &lt;br /&gt;
Ruvu (at Moro Bridge) 	1,370 &lt;br /&gt;
Wami (at Mandera) 	3,280 &lt;br /&gt;
Ruhuhu (at Kikonge) 	5,600 &lt;br /&gt;
Kiwira (at Kyela) 	1,900 &lt;br /&gt;
Kagera (at Kyaka) 	7,064 &lt;br /&gt;
Mara (at Mara Mines) 	1,971 &lt;br /&gt;
Pangani (at Hale) 	627 &lt;br /&gt;
(Source: NWSDS, 2008)&lt;br /&gt;
 &lt;br /&gt;
&lt;br /&gt;
The most abundant surface water resources exist in Lakes Victoria, Tanganyika, Nyasa, Chala and Jipe, as well as the Kagera, Mara and Songwe rivers, which are trans-boundary waters. The use of these abundant surface water resources for water supply, irrigation and other purposes is still very limited even today.&lt;br /&gt;
&lt;br /&gt;
Tanzania is also rich in wetland systems that are areas which, for part of the year, have enough water to enable the development of types of plants and animals adapted to these conditions.  These include the lakes of the Western and Eastern Rift Valley system, Lake Victoria, numerous small lakes, riverine flood plains and permanent swamps, coastal mangrove and deltaic systems, and a number of artificial impoundments and reservoirs and fish ponds.  There are numerous permanent and seasonal freshwater swamps and flood plains distributed in almost all of the country's major drainage basins, which account for some 2.7 million hectares.  The largest in this category are found in the Rufiji/Ruaha river system and in the Malagarasi/Moyowosi system, while other river systems are the Kagera River, along with Ugalla River, Suiwe River, Mara River, Pangani, Wami and Ruvu Rivers. The principal wetlands of Tanzania constitute one of the country's richest and most durable resources. &lt;br /&gt;
&lt;br /&gt;
3.2	Water Sources Available in Tanzania Mainland&lt;br /&gt;
In Tanzania, there are three main categories of water sources available, namely rainwater, surface and groundwater. &lt;br /&gt;
&lt;br /&gt;
3.2.1	Rainwater and fog harvesting&lt;br /&gt;
One of sources of water include rainwater and fog that can generate limited amounts of very clean water if they are properly collected and stored. In an area where other water sources are not available, consideration should be given to harvesting rainwater and fog.&lt;br /&gt;
&lt;br /&gt;
3.2.2	Surface Water&lt;br /&gt;
For design purposes, the surface water sources that can be considered include;&lt;br /&gt;
•	Rivers or streams,&lt;br /&gt;
•	Impoundments (Reservoirs and ponds),&lt;br /&gt;
•	Springs,&lt;br /&gt;
•	Lakes,&lt;br /&gt;
•	Dams (charco, sand, earth etc).&lt;br /&gt;
&lt;br /&gt;
A brief description of each water source is provided below.&lt;br /&gt;
&lt;br /&gt;
3.2.2.1	 Rivers or streams &lt;br /&gt;
Rivers and streams are water sources that originate from springs located in highlands which flow down to the end of the respective drainage basin which can be lakes, seas or oceans as depicted on the map of Tanzania in Figure 3.1. &lt;br /&gt;
3.2.2.2	 Impoundments&lt;br /&gt;
Impoundments includes all types of reservoirs that emanate from road borrow pits, mining, human or natural activities that are utilised as sources of water for a formal water supply project. &lt;br /&gt;
3.2.2.3	 Springs&lt;br /&gt;
Springs include artesian or freely flowing spring water that has been tapped by an intake structure to facilitate supply of water to a designated community. Spring is a point where groundwater flows out of the ground, and is thus where the aquifer surface meets the ground surface. A spring may be ephemeral (intermittent) or perennial (continuous). Springs can be developed by enlarging the water outlet and constructing an intake structure for water catchment and storage. &lt;br /&gt;
&lt;br /&gt;
3.2.2.4	Lakes &lt;br /&gt;
Lakes found in Tanzania are either located at the end of drainage basins or are highland lakes and some of them are volcanic lakes. Tanzania is endowed with many small inland lakes apart from the third biggest lake in the world (Lake Victoria) as well as Lake Tanganyika which is the world’s deepest lake. Both lakes supply water to various localities around their respective catchments.&lt;br /&gt;
3.2.2.5	 Dams &lt;br /&gt;
Dams are classified based on the availability of construction materials. Various types of dams can be built ranging from earth fill dams, concrete dams, sand dams and charco dams. These are purposely built structures that allow impoundment of river and/or rain water for various end uses. &lt;br /&gt;
&lt;br /&gt;
3.2.3	Groundwater&lt;br /&gt;
Groundwater is that portion of rainwater which has percolated beneath the ground surface to form an underground reservoir referred to as aquifer water. The upper surface of groundwater is the water table. Groundwater is often clear, free from organic matter and bacteria due to the filtering effect of the soil on water percolating through it. However, groundwater almost always contains dissolved minerals from the soil. Groundwater is often better in terms of quality than surface waters. It is less expensive to develop for use, and usually provides more adequate supply in many areas in the country. In semi-arid and the drier parts of the country,  groundwater has played and will continue to play a major role as the sole water source for various uses especially in the central and northern parts of the country and the drier regions of Dodoma, Singida, Shinyanga, Tabora, Mwanza, Mara, Arusha, Coast and Southern Kilimanjaro.&lt;br /&gt;
&lt;br /&gt;
Groundwater can be considered as either spring water or well (or borehole) water. Springs, offer excellent water supply opportunities, but are generally found in hilly or mountainous areas only. They may require long pipelines in order to bring the water to the demand area. This is a feasible source for larger and concentrated settlements but rarely for dispersed populations. For rural water supply systems, groundwater is generally preferred as a water source. &lt;br /&gt;
&lt;br /&gt;
The main sub-types of groundwater and extraction methods are as follows:&lt;br /&gt;
&lt;br /&gt;
3.2.3.1	 Infiltration galleries/wells &lt;br /&gt;
Infiltration galleries are horizontal wells, constructed by digging a trench into the water-bearing sand and installing perforated pipes in it. Water collected in these pipes converges into a “well” from which it is pumped out. &lt;br /&gt;
3.2.3.2	 Well&lt;br /&gt;
This is a hole constructed by any method such as digging, driving, boring, or drilling for the purpose of extracting water from underground aquifers. Wells can vary greatly in depth, water volume and water quality. Well water typically contains more minerals in solution than surface water and may require treatment to soften the water by removing minerals such as arsenic, iron and manganese. Well water may be drawn by pumping from a source below the surface of the earth. Alternatively, it could be drawn up using containers, such as buckets that are raised mechanically or by hand.&lt;br /&gt;
&lt;br /&gt;
Wells are various types of artificially constructed water production wells that are designated as shallow wells (up to 20 metres deep) or deep wells (more than 20 metres deep) as designated by the Ministry responsible for water from time to time.  Water is pumped out of the well into the end user containers or a storage tank using various types of pumps that can be driven manually or using various energies. Typical cross sections through such wells are given in Section 3.6.5.&lt;br /&gt;
3.2.3.3	Classification of wells based on the aquifer tapped&lt;br /&gt;
As mentioned, an aquifer contains a considerable amount of groundwater underground beneath layers of permeable soil material like sand or gravel. Aside from their water storage capacity, aquifers allow the underground flow of groundwater. Aquifers are recharged with rainwater that seeps down to the soil and through the permeable layers.&lt;br /&gt;
3.2.3.3.1	Shallow wells&lt;br /&gt;
Generally, a well is considered shallow if it is less than 20 metres deep. Shallow wells tap the upper water-bearing layer underground. This permeable layer, however, usually has limited safe yield due to its great dependence on seasonal rainfalls. Therefore, the supply capacity of shallow wells could be unreliable and are sometimes intermittent. Also, the water extracted from the upper strata is usually more affected by contamination since the aquifer being tapped is near the ground surface where possible sources of contamination are abound. Protection against contamination is therefore one of the main considerations in constructing a shallow well.&lt;br /&gt;
3.2.3.3.2	Deep wells&lt;br /&gt;
Deep wells, which are over 20 metres deep, tap the deeper unconfined aquifer. This aquifer is not confined by an overlying impermeable layer and is characterized by the presence of a water table. A deep well is less susceptible to surface contamination because of the deeper aquifer. Also, its yield tends to be more reliable since it is less affected by seasonal precipitation.&lt;br /&gt;
&lt;br /&gt;
3.2.3.3.3	Artesian wells&lt;br /&gt;
Artesian wells are much like the deep wells except that the water extracted is from a confined aquifer. The confining impermeable layers are above and below the aquifer. Groundwater recharge enters the aquifer through permeable layers at high elevations causing the confined groundwater at the lower elevations to be under pressure. In some cases, the hydraulic pressure of the aquifer is sufficient for a well to flow freely at the well head.&lt;br /&gt;
&lt;br /&gt;
3.3	Quality Suitability of Water Sources for Water Supply Projects&lt;br /&gt;
When considering the different water sources for water supply projects, it is necessary to ensure that the quality of the water source expected to be utilised is monitored well preferably for a period of not less than three years consecutively to ensure the variability of the quality is captured during the wet and dry seasons. When one looks at the list of the potential sources presented in the foregoing section, such a monitoring programme may not be necessary for rainwater and fog. Only short-term monitoring of the quality of these two sources should be undertaken.&lt;br /&gt;
&lt;br /&gt;
3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment&lt;br /&gt;
&lt;br /&gt;
A decision on whether the water source needs to be subject to water treatment or otherwise will emanate from the results of the short term tests on the quality of the water which will in turn guide the decision of pilot testing the recommended flow sheets particularly for river/streams, lakes, impoundments and dams. Groundwater will usually need only a few unit operations for removal of the identified elevated impurities that may include Iron, Manganese or Fluoride and the need to disinfect water from shallow wells in addition to maintaining residual disinfectants for prevention of re-contamination. Rainwater and condensates from fog will not need to be pilot tested.&lt;br /&gt;
&lt;br /&gt;
3.5	General Considerations for Selection of Water Sources &lt;br /&gt;
In the selection of a source or sources of water supply, adequacy and reliability of the available supply can be considered as the overriding criteria. Without these, the water supply system cannot be considered viable. These, together with the other factors that should be considered (and which are interdependent), are as follows:&lt;br /&gt;
&lt;br /&gt;
3.5.1	Adequacy and reliability&lt;br /&gt;
Adequacy of water supply requires that the quantity of water flow of water source be large enough to meet present and future water demand. On the other hand, source reliability can be expressed by how frequently a water system expects normal demand to go unmet, such as a one-in -25 year or even a one-in-50 year drought. Safe yield is a 1-day low flow rate that is exceeded for 96 percent of the period of record and that can be related to the determined average daily water demand in order to establish the reliability of a water source. For a river/stream, safe yield represents the minimum flow rate that will guarantee no risk to the river hydrology and its surroundings. Safe yield is estimated so as to check whether the planned withdrawal for water supply purposes will be met. To determine the safe yield of a river or stream, a flow -frequency/probability analysis presented in section 3.1.5.5 should be performed. From the analysis, the determined 96 % low flow index should be taken as the safe yield of the river or stream and thus considered as the water source reliability.&lt;br /&gt;
&lt;br /&gt;
3.5.2	Quality of water sources&lt;br /&gt;
The assessment of water quality of a water source is important to establish the suitability of water source for human consumption. The quality of surface water is determined by the amount of pollutants and contaminants picked up by the water in the course of its travel. While flowing over the ground, surface water collects silt, decaying organic matter, bacteria and other micro-organisms from the soil. Sources which require little or no treatment of the water should be chosen in the first instance, provided the required quantity of water can be obtained. Hence springs and ground water resources should always be exploited in the first hand. Surface water from rivers, streams and lakes will almost always require some treatment to render it safe for human consumption. However, for large supplies, surface water will often still be the most economical alternative. Rivers which have the bulk of their catchments in forest areas should be preferred.&lt;br /&gt;
&lt;br /&gt;
Thus, all surface water sources should be presumed to be unsafe for human consumption without some form of treatment. The option to treat surface water to make it safe for human consumption in compliance with the latest edition of Tanzania potable water standards (TBS, TZS 789) has to be evaluated to decide on the feasibility of the water supply project.&lt;br /&gt;
&lt;br /&gt;
3.5.3	Technical Requirements&lt;br /&gt;
The development of the source should be technically feasible, the operation and maintenance requirements for the source abstraction and supply system should be appropriate to the resources available.&lt;br /&gt;
&lt;br /&gt;
3.5.4	Cost implications to develop a water source&lt;br /&gt;
The assessment of investment costs to develop a given water source including operation and maintenance costs has a bearing in the selection of the water source for development. Affordability of investment costs is an important factor to be considered in the selection of the water source.&lt;br /&gt;
&lt;br /&gt;
3.5.5	Protection of water sources&lt;br /&gt;
The location of a water source is a key factor in securing the highest quality water source. In analysing a source location, the design engineer should consider the measures necessary to protect the water source from human excreta, from industrial discharges and from agricultural run-off. In addition, measures to establish and maintain watershed control, physical protection and barriers to contamination have to be considered to ensure sustainable quantity and quality of the raw water.&lt;br /&gt;
&lt;br /&gt;
3.5.6	Legal and management requirements&lt;br /&gt;
Ownership of the land and the legal requirements of obtaining permission to abstract are also factors to consider when selecting a source. Sources on private land may cause access problems.&lt;br /&gt;
&lt;br /&gt;
3.5.7	Distance of water supply source&lt;br /&gt;
The source of the water supply must be situated as near to the demand area as possible. Hence, less length of pipes needs to be installed and thus economical transfer and supply of water. The source(s) nearest to the demand area is usually selected.&lt;br /&gt;
&lt;br /&gt;
3.5.8	Topography of the project area and its surroundings&lt;br /&gt;
The area or land between the source and the area to be served by water supply system should not be highly uneven, i.e., it should not have steep slopes because cost of construction or laying of pipes is very high in such areas.&lt;br /&gt;
&lt;br /&gt;
3.5.9	Elevation of a source of water supply&lt;br /&gt;
The source of water must be on a high elevation than the demand area so as to provide sufficient residual pressure in the water for daily requirements. When the water is available at lower levels, then pumps are used to pressurize water. This requires an excess developmental and operational tasks and costs.&lt;br /&gt;
&lt;br /&gt;
3.6	Determination of water source yield&lt;br /&gt;
Sources which require little or no treatment of raw water such as springs, wells and boreholes should be given the highest selection priority provided their yields are sufficient to meet the water demands of the water supply scheme. For large supplies, surface water will continue to be the most economical alternative water source. In selecting surface water sources, rivers with upland and mostly forested catchments should be given preference. Sub-surface water drawn from a riverbed or river bank can sometimes be a viable alternative in dry areas with only seasonal flows in the river, or in rivers with a high silt load.&lt;br /&gt;
&lt;br /&gt;
Sources from which water can be supplied by a gravity system are particularly more favourable than those which require pumping with significant energy costs. For household and small community water supplies, rainwater harvesting will be the most appropriate in most medium and high potential areas in Tanzania that receive sufficient rains.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
3.6.1	Rainwater and fog harvesting&lt;br /&gt;
3.6.1.1	 Rainwater harvesting&lt;br /&gt;
Rainwater harvesting is a technique of collection and storage of rainwater into natural reservoirs or tanks, or the infiltration of surface water into subsurface aquifers (before it is lost as surface runoff). Types of rainwater harvesting systems are described in the sections below.&lt;br /&gt;
&lt;br /&gt;
3.6.1.1.1	Types of rainwater harvesting&lt;br /&gt;
Two types of rainwater harvesting should be considered:&lt;br /&gt;
&lt;br /&gt;
•	Land catchment,&lt;br /&gt;
•	Roof catchment.&lt;br /&gt;
&lt;br /&gt;
Important data for design of rainwater harvesting systems:&lt;br /&gt;
•	Rainfall data&lt;br /&gt;
•	Catchment/Surface Area &lt;br /&gt;
•	Run-off Coefficient&lt;br /&gt;
&lt;br /&gt;
To accurately estimate the potential rainwater supply from a catchment, reliable rainfall data for a 10-year period is required . The Hydrology Section, Tanzania Meteorology Agency, and Agriculture Departments should be contacted for rainfall data wherever rainwater-harvesting technology is proposed. &lt;br /&gt;
&lt;br /&gt;
The amount of rainfall collected depends on the surfaces where rain falls and the runoff coefficient K of the surface. The runoff coefficient varies with topography, land use, vegetation cover, soil type and moisture content of the soil. In selecting run off coefficients the future characteristics of the water shed are considered. If land use varies within a water shed consider the segments individually and use a weighted coefficient value to determine the total runoff for the watershed. Practically annual rainfall falls during the rainy seasons between October and May.&lt;br /&gt;
&lt;br /&gt;
(i) Run-off Coefficients&lt;br /&gt;
Table 3:2 shows the runoff coefficients for various surfaces. They should be used for calculating the fraction of the rainfall which can be harvested.&lt;br /&gt;
&lt;br /&gt;
Table 3.2: Run-Off Coefficients for Different Surfaces&lt;br /&gt;
SURFACE	RUN-OFF&lt;br /&gt;
COEFFICIENT (K)&lt;br /&gt;
1.	Roof catchments	&lt;br /&gt;
	•	Roof tiles	0.8 to 0.9&lt;br /&gt;
	•	Corrugated sheets	0.7 to 0.9&lt;br /&gt;
2.	Ground surface covering&lt;br /&gt;
	•	Concreted	0.6 to 0.8&lt;br /&gt;
	•	Bitumen, plastic sheeting, butyl rubber	0.8 to 0.9&lt;br /&gt;
	•	Pavement of stone, bricks with open joints	0.5 to 0.6&lt;br /&gt;
	•	Pavement of stone, bricks with tightly cemented joints	0.75-0.85&lt;br /&gt;
3.	Compacted and smoothened soil	0.3 to 0.5&lt;br /&gt;
4. Lawns, sandy soil&lt;br /&gt;
	•	2% slope	0.05-0.10&lt;br /&gt;
	•	2.7% slope	0.10-0.15&lt;br /&gt;
	•	&amp;gt;7%	0.15-0.20&lt;br /&gt;
5. Lawns, heavy soil&lt;br /&gt;
	•	2% Slope	0.13-0.17&lt;br /&gt;
	•	2.7% slope	0.18-0.22&lt;br /&gt;
	•	&amp;gt;7%	0.25-0.35&lt;br /&gt;
6.	•	Uncovered surface, flat terrain	0.3&lt;br /&gt;
	•	Uncovered surface, slope less than 10%	0.0 to 0.4&lt;br /&gt;
	•	Rocky natural catchments	0.2 to 0.5&lt;br /&gt;
&lt;br /&gt;
3.6.1.1.2	Components of rainwater harvesting system&lt;br /&gt;
a) Catchments Area: The catchment of a water harvesting system is the surface which directly receives the rainfall and provides water to the system.&lt;br /&gt;
b) Coarse mesh at the roof to prevent the passage of debris.&lt;br /&gt;
c) Gutters to collect and transport rainwater to the storage tank. Gutters can be semi-circular or rectangular and could be made using:&lt;br /&gt;
&lt;br /&gt;
•	Locally available material such as plain galvanised iron sheet (20 to 22 gauge), folded to required shapes &lt;br /&gt;
•	Semi-circular gutters of PVC material can be readily prepared by cutting those pipes into two equal semi-circular channels.&lt;br /&gt;
•	Bamboo trunks cut vertically in half&lt;br /&gt;
&lt;br /&gt;
The size of the gutter should be according to the flow during the highest intensity rain. It is advisable to make them 10 to 15 per cent oversize.&lt;br /&gt;
&lt;br /&gt;
d) Conduits/pipeline that carry rainwater from the catchment or rooftop area to the harvesting system. Conduits can be of any material like polyvinyl chloride (PVC) or galvanized iron (GI), materials that are commonly available.&lt;br /&gt;
&lt;br /&gt;
e) First Flush pipe to separate first rainwater contaminants namely debris, dirt, and dust.&lt;br /&gt;
&lt;br /&gt;
3.6.1.1.3	Estimation of the yield&lt;br /&gt;
A first estimate of the average yield of a catchments area can be found using the following expression.&lt;br /&gt;
S = K × I × A						(3.1)&lt;br /&gt;
Where: &lt;br /&gt;
S = Yield in m3 / annum &lt;br /&gt;
A = Area of catchment/surface, m2 &lt;br /&gt;
I = Average annual rainfall m/annum &lt;br /&gt;
K = runoff coefficient &lt;br /&gt;
&lt;br /&gt;
Determination of average runoff coefficient for the entire catchment area composed of different surfaces can be calculated as follows:&lt;br /&gt;
 +...					(3.2)&lt;br /&gt;
The required capacity of the collection facility should be calculated using available meteorological data showing the rainfall pattern of the area. However, for rough calculations the storage tank, capacity may be calculated as follows:&lt;br /&gt;
C = D × T × 10-3						(3.3)&lt;br /&gt;
&lt;br /&gt;
Where:&lt;br /&gt;
C = Capacity of tank in m3 &lt;br /&gt;
D = Total water demand in litres / day&lt;br /&gt;
T = Longest dry spell in days&lt;br /&gt;
&lt;br /&gt;
3.6.2	Hydrological Analysis of Surface Waters&lt;br /&gt;
The Design Manual for Water Supply projects is expected to reflect the best concepts on what constitutes the basis for designing a safe, reliable and sustainable water system. Hydrological principles must be taken into consideration during the feasibility and preliminary design stages of the water supply system to ensure that from the outset, design and construction of the system is done right. The design engineer must apply hydrological principles during design of the water system to ensure that the system being designed does not result in exhausted water supply sources and empty reservoirs after construction of the project is completed. If it is recognised from the beginning that there is water deficiency from the source, then the water source should not be considered for development.&lt;br /&gt;
&lt;br /&gt;
The following steps should be followed when undertaking hydrological analysis for the water supply projects:&lt;br /&gt;
&lt;br /&gt;
Step 1: Measurement of the quantity of surface water sources,&lt;br /&gt;
Step 2: Low flow assessment of surface water sources,&lt;br /&gt;
Step 3: Flood flow estimation,&lt;br /&gt;
Step 4: Rainfall analysis,&lt;br /&gt;
Step 5: Water permit application,&lt;br /&gt;
Step 6: Data to support hydrological analysis.&lt;br /&gt;
&lt;br /&gt;
Step 1: Measurement of River Discharge&lt;br /&gt;
In order to assess the amount of water available from the identified surface water source, a discharge measurement must be carried out during both the dry and wet seasons. Measurement of discharge will highlight the production capacity of a water source, the information which is important in the planning of a water system. An estimate of the quantity of water that can be reliably produced by a water source gives the planner a basis to decide for or against its development. For the sources to be considered adequate, they must at least satisfy the average day water demand of the area to be served by a water system. The average daily water demand is calculated from estimated average water requirements for domestic, commercial, industrial, public institutions and livestock. The following methods can be used to measure discharge.&lt;br /&gt;
&lt;br /&gt;
a) Volumetric Method&lt;br /&gt;
This method is appropriate for measuring small quantities of flow from small streams and springs. Flow can be measured by measuring the volume. The equipment required are a stop watch and a bucket or drum of known volume. The method consists of determining the time required to fill the bucket or drum. For more accurate results, the measurement is repeated several times, and the average time of these trials is taken.&lt;br /&gt;
&lt;br /&gt;
b) V-Notch Weir Method&lt;br /&gt;
A weir is an overflow structure built across an open channel for the purpose of measuring the rate of flow. Weirs may be rectangular, trapezoidal or triangular in shape. The triangular or V-Notch Weir is a flow measuring device particularly suited for small flows. The V-Notch Weir often used in flow measurements is the 90° V-Notch that is placed in the middle of the channel and water is allowed to flow over it. The water level in the channel is then measured using a gauging rod. The zero point in the rod should be level with the sill or crest of weir/notch. For a known height of water above the zero in the rod, the flow in cumecs for the 90° V-Notch can be obtained by using the formula:&lt;br /&gt;
&lt;br /&gt;
 							(3.4)&lt;br /&gt;
&lt;br /&gt;
 								(3.5)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
Q = Discharge in m3/sec&lt;br /&gt;
H =Height of Water level above the crest of the weir in meters&lt;br /&gt;
In this case, the discharge coefficient of the weir is approximated to be equal to 0.58.&lt;br /&gt;
&lt;br /&gt;
c) Current meter Measurement&lt;br /&gt;
The current meter is an instrument that is used to measure relatively larger quantities of flow from streams and rivers. The instrument consists of a propeller rotating freely on a well-lubricated shaft. The device is lowered into the water and the rate of revolution of the impeller is directly proportional to the velocity of the water flow. A small magnet is usually built into the shaft of the instrument and a coil detects the passage of the magnet and allows the number of revolutions of the shaft in the given time to be counted. Once the rate of revolution of the impeller is known the water velocity can be calculated using the calibration equation for the instrument, which is expressed as follows:&lt;br /&gt;
&lt;br /&gt;
 									(3.6)&lt;br /&gt;
&lt;br /&gt;
Where, &lt;br /&gt;
V is the water velocity in meters per second&lt;br /&gt;
n is the number of revolutions of the impeller per second&lt;br /&gt;
a, b are constants for the particular instrument.&lt;br /&gt;
&lt;br /&gt;
The discharge measurement using the current meter at the time of measurement, Q,  is  determined by multiplying the velocity of flow and water flow cross-section area.&lt;br /&gt;
&lt;br /&gt;
Step 2: Low flow assessment&lt;br /&gt;
The assessment of low flow magnitudes of streams/rivers or springs in hydrology is important in the planning of a water supply system in view of the fact that it reflects on the water source adequacy and reliability to meet the consumer demand. In low flow hydrology, two questions are asked about a particular river identified to be a water source for a given water supply system:&lt;br /&gt;
&lt;br /&gt;
(i)	Does the river supply a particular water demand at all times?&lt;br /&gt;
(ii)	If not, how much water must be stored in order to meet any deficiency which may arise?&lt;br /&gt;
&lt;br /&gt;
Techniques of flow duration curves, annual minimum flow analyses and annual drought volumes are applied to address the two questions.&lt;br /&gt;
&lt;br /&gt;
a) Flow duration curve&lt;br /&gt;
The flow-duration curve (FDC) is defined as a cumulative frequency curve that shows the percent of time specified discharges were equalled or exceeded during a given period. It combines in one curve the flow characteristics of a stream throughout the range of discharge, without regard to the sequence of occurrence. To prepare a flow-duration curve, the daily, weekly, or monthly flows during a given period are arranged according to magnitude, and then percent of time during which specified flow values are equalled or exceeded are computed. &lt;br /&gt;
&lt;br /&gt;
A flow duration curve once it is prepared, is used to determine the indices of low flow magnitudes; for example, the 96-percentile flow (Q96), is the flow that is exceeded for 96 percent of the period of record. This discharge value is a useful index of low flow that is related to the quantity of water that can be available for water supply in the dry season.&lt;br /&gt;
&lt;br /&gt;
The following steps are followed to construct the FDC:&lt;br /&gt;
&lt;br /&gt;
(i)	Rank the observed stream flows in descending order (from the maximum to the minimum value).&lt;br /&gt;
(ii)	Calculate exceedance probability (P) of each flow as follows:&lt;br /&gt;
&lt;br /&gt;
		 						(3.7)&lt;br /&gt;
&lt;br /&gt;
		Where,&lt;br /&gt;
			P is the probability that a given flow will be equalled or exceeded 			(% of time),&lt;br /&gt;
			m is the ranked position of a given flow value on the list,&lt;br /&gt;
			n is the length of the sample.&lt;br /&gt;
&lt;br /&gt;
(iii)	 A FDC is obtained by plotting each ordered observed streamflow value versus the corresponding calculated exceedance probability.&lt;br /&gt;
(iv)	 Read the indices of low flow magnitudes from the FDC corresponding to 90%, 95% and 99% probabilities of exceeded.&lt;br /&gt;
&lt;br /&gt;
b) Low flow frequency analysis&lt;br /&gt;
The frequency analysis of low river flows is performed by analyzing 1-day or 7-day or 10-day annual minimum flow series obtained by selecting the lowest flow values occurring in each year of record. The set of observed annual minimum flow values recorded at any gauging station is assumed to be a random statistical sample from the population of all possible annual minima at the given site.&lt;br /&gt;
&lt;br /&gt;
The selected set of observed annual minimum flow values is fitted to the Gumbel statistical distribution and then the annual minimum flow magnitudes (QT) corresponding to the design probability of failure (1/T) is then estimated from the Gumbel prediction equation:&lt;br /&gt;
&lt;br /&gt;
 								(3.8)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
QT = Low flow magnitude&lt;br /&gt;
T = Return period of one failure in T years&lt;br /&gt;
  and  = Gumbel Parameters &lt;br /&gt;
KT = Frequency factor, obtained as:&lt;br /&gt;
&lt;br /&gt;
 							       (3.9)&lt;br /&gt;
&lt;br /&gt;
Results from low flow frequency analysis:&lt;br /&gt;
(i)	If the value of QT is large in comparison to QD, the average day water demand, then the river can be considered to be able to supply the demand satisfactorily.&lt;br /&gt;
(ii)	On the other hand if QT is less than or of the same order of magnitude as, QD, ,then the river alone without some form of flow regulation could not be considered satisfactory for supplying the demand. &lt;br /&gt;
&lt;br /&gt;
c) Annual drought volumes Analysis&lt;br /&gt;
On the basis of the results obtained from low flow frequency analysis, in case the annual minimum flow magnitudes (QT) corresponding to the design probability of failure (1/T) is found to be less than QD, demand flow, then storage will be required to meet the established water demand. The required storage is determined by carrying out deficiency/drought Volumes Analysis.&lt;br /&gt;
&lt;br /&gt;
The storage required on a river to meet a specific demand depends on the following factors:&lt;br /&gt;
&lt;br /&gt;
•	Variability of the river flow&lt;br /&gt;
•	Magnitude of the demand&lt;br /&gt;
•	Degree of reliability of meeting the demand&lt;br /&gt;
&lt;br /&gt;
The capacity of the reservoir required to augment the river flow in any year can  be determined from the analysis of the series of annual maximum deficiencies (drought volumes) as follows:&lt;br /&gt;
&lt;br /&gt;
Drought volumes V1, V2, V3,…, Vn are computed from a hydrometric record of the river flow (Qi), with reference to the demand flow (QD), i.e., (Vi = Qi-QD). &lt;br /&gt;
&lt;br /&gt;
The set of observed annual maximum deficiencies at any gauging station is assumed to be a random statistical sample. The annual maximum deficiency (VT) corresponding to the probability of failure (1/T) is estimated from the series of annual maximum deficiencies using a statistical distribution, e.g., Gumbel distribution as illustrated in previous section. The design storage of the reservoir can be made equal to the volume VT corresponding to a risk of one failure in T years. &lt;br /&gt;
&lt;br /&gt;
Step 3: Dependable Rainfall Analysis&lt;br /&gt;
Rainfall analysis is carried out when the need arises to determine dependable rainfall in a given area for the purpose of designing a rainwater harvesting system for domestic use. Frequency analysis of recorded annual rainfall data from a given area, enables the determination of the 90% dependable annual rainfall. This is the value of rainfall magnitude that will be exceeded 90% of the time. In the design of Rainwater Water Harvesting system, catchment (i.e. roof) area and depth of rainfall are important parameters for estimation of optimal storage size. Taking note of the fact that rainfall amounts vary on a year to year basis, the computed rainfall magnitude that is exceeded 90% of the time, is taken as the value of annual rainfall depth that can be expected to occur with some degree of certainty and thus used in the design. The exceedance probability is determined by ranking the observed annual rainfall in ascending order (from the minimum to the maximum value) and then calculating non-exceedance probability (P) as follows:&lt;br /&gt;
&lt;br /&gt;
 								(3.10)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
P is the probability that a given rainfall will be equalled or not exceeded (% of time),&lt;br /&gt;
m is the ranked position of a given rainfall value on the list,&lt;br /&gt;
n is the length of the sample.&lt;br /&gt;
&lt;br /&gt;
The probability of dependable rainfall is obtained by calculating  the value of exceedance probability (1 – P).&lt;br /&gt;
&lt;br /&gt;
Step 4: Flood flow estimation for intakes and small dams' spillways&lt;br /&gt;
The need to estimate flood peaks or design floods arises where it is required to design a spillway of a dam proposed for water storage and also the design of water intake structures. Water intakes and spillway of small dams are designed to accommodate the 100-year flood. &lt;br /&gt;
&lt;br /&gt;
Frequency analysis of observed Annual Maximum streamflow records from a gauging station enables the estimation of flood peaks. The statistical distribution namely the Gumbel distribution or other statistical distribution used in Tanzania such as Pearson type 3, Log-Pearson type 3, Log-Normal and General Extreme Value can be used to carry out frequency analysis in order to determine the magnitude of flood peak of 100-year required for the design. The estimation of design flood peak magnitudes for specified return periods using the Gumbel Distribution is illustrated below.&lt;br /&gt;
&lt;br /&gt;
Prediction equation&lt;br /&gt;
&lt;br /&gt;
 								(3.11)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
QT = Flood peak magnitude&lt;br /&gt;
T = Return period of one failure in T years&lt;br /&gt;
  and  = Gumbel Parameters&lt;br /&gt;
KT = Frequency factor, obtained as:&lt;br /&gt;
&lt;br /&gt;
 							(3.12)&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
Estimation of Gumbel parameters by Method of Moments (MoM)&lt;br /&gt;
&lt;br /&gt;
Mean,  							(3.13)&lt;br /&gt;
Standard deviation,  α						(3.14)		&lt;br /&gt;
&lt;br /&gt;
The mean, μ and Standard Deviation values, σ are computed from observed annual maximum streamflow records. Note that other frequency distributions (Pearson type 3, Log-Pearson type 3, Log-Normal and General Extreme Value) have different expressions for estimating the distribution parameters.&lt;br /&gt;
&lt;br /&gt;
Step 5: Application for water permit&lt;br /&gt;
Water abstraction for water supply from a river or spring requires a permit from the respective water basin office. The planner of the water supply project must apply for the water permit abstraction early in the project design because it can affect the viability of a project. The design engineer must seek the water permit if the project involves a new, replacement, increased withdrawal from a source or an increase in the water system’s physical capacity.&lt;br /&gt;
&lt;br /&gt;
Step 6: Environmental flow considerations&lt;br /&gt;
Environmental flow may be computed in terms of magnitude, timing of low flow in the dry month, duration of low flow in days, frequency of occurrence of the low flow event (return period) and rate of change of low flow over time (m3/day of flow recession). The recommended environmental flow varies for individual rivers and streams and therefore to determine its flow value, a comprehensive Environmental Impact Assessment (EIA) should be conducted and approved by NEMC. Also, there are some guidelines and procedures for environmental flow assessment for specific catchments in Tanzania developed by NEMC. Accordingly, designers need to consult NEMC for environmental flow information in their project areas (https://www.nemc.or.tz/).&lt;br /&gt;
&lt;br /&gt;
Step 7: Data to support hydrological analysis&lt;br /&gt;
Hydrological data is invaluable for planning of water supply systems. For example, water source adequacy and reliability can be determined from analysis of streamflow data which is important hydrological data. Hydrological data expected to be collected by water basin offices in Tanzania to support the planning of water supply systems, specifically to answer questions related to the following:&lt;br /&gt;
&lt;br /&gt;
•	Water availability in terms of quantity and quality&lt;br /&gt;
•	Frequency of occurrence of low flows and flood flows&lt;br /&gt;
•	Variability of flow regime in terms of quantity and quality&lt;br /&gt;
&lt;br /&gt;
Important data to be collected include the following:&lt;br /&gt;
&lt;br /&gt;
(i)	Streamflow – required to quantify available water and estimate flood peaks and low flow magnitudes,&lt;br /&gt;
(ii)	Rainfall – required to determine 90% dependable rainfall,&lt;br /&gt;
(iii)	Sediment - Sediment deposition affects the water carrying capacity of rivers and the useful life of reservoirs. Sediment data is required to determine the useful reservoir capacity and the life span of the reservoir.&lt;br /&gt;
(iv)	 Climate data - (Evaporation, Temperature, Wind speed, sunshine hours, radiation and humidity) – required to estimate water loss from reservoirs.&lt;br /&gt;
&lt;br /&gt;
During the feasibility and preliminary design stage, the design engineer must look for streamflow records from stream gauging stations located at or near water intakes and dam sites to support the design work. In a situation where there are no gauging stations at or near water intakes or dam sites, two options may be considered to get flow data to be used in the design.&lt;br /&gt;
&lt;br /&gt;
Option 1: Transfer data from adjacent or neighbouring drainage areas that have comparable or similar characteristics. The same applies to a situation where rainfall data is missing, rainfall data from adjacent or similar catchments is used to derive flow frequency/probability curves required in the design of water supply system.&lt;br /&gt;
Option 2: Install permanent or temporary gauging stations and start recording flow data at the earliest possible time during the planning steps of the water supply project.&lt;br /&gt;
&lt;br /&gt;
3.7	Other considerations for various water sources&lt;br /&gt;
3.7.1	Water permits Considerations&lt;br /&gt;
During the course of implementation of water supply projects, designers will need to work with the relevant Water Basin Authorities and relevant catchment and sub-catchment committees to ensure all water users with water withdrawal permits are considered during the course of sizing the projects to ensure no developmental constraints are faced as a result of ignoring other users. It will be necessary to consult the updated water permits registers maintained by each Basin Water Board prior to planning expansion of any new water supply project.&lt;br /&gt;
&lt;br /&gt;
3.7.2	Conservation of water sources&lt;br /&gt;
In line with NAWAPO, the protection and conservation of water sources is one of the main duties of all the Basin Water Boards.  Intuitively, for national water resources the MoW also has the responsibility to deal with resolution of all water use conflicts. It will ensure that the WRM Act No.11 of 2009 as well as the associated regulations are fully observed by all parties. Other relevant laws such as those associated with pollution coordinated by other agencies or bodies like the National Environment Management Council (NEMC) are observed with respect to water resources. Where transboundary water resources are involved, the MoW has to ensure the protection roles that are expected of Tanzania are properly fulfilled in line with the relevant international laws, agreements or conventions stated in section 1.1.4.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
3.8	References&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=Chapter_Three:_Water_Sources_Analysis&amp;diff=519</id>
		<title>Chapter Three: Water Sources Analysis</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=Chapter_Three:_Water_Sources_Analysis&amp;diff=519"/>
		<updated>2020-03-31T10:57:51Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;Water source forms one single most important element and is a key to proper function and thus sustainability of any water supply project. Evidence shows that whenever proper water source analysis has not been adequately conducted, most of water supply projects fall into dysfunction. Thus, this chapter presents the analysis of water sources. It includes analysis of both surface and ground water. Further, the chapter gets into 'nitty gritty' of each of this category.&lt;br /&gt;
&lt;br /&gt;
==3.1	Availability of Water Resources in Tanzania Mainland==&lt;br /&gt;
Tanzania mainland is endowed with a wide range of water resources that includes the main drainage systems, river basins and natural wetlands that are identified in the next paragraphs. With respect to the drainage systems of water resources in Tanzania mainland, it is divided into five drainage systems that include:&lt;br /&gt;
* The Indian Ocean drainage system,&lt;br /&gt;
* The Internal drainage system to Lake Eyasi, Natron and Bubu depression,&lt;br /&gt;
* The Internal drainage systems to Lake Rukwa,&lt;br /&gt;
* The Atlantic Ocean drainage system through Lake Tanganyika, &lt;br /&gt;
* The Mediterranean Sea drainage system through Lake Victoria.&lt;br /&gt;
&lt;br /&gt;
The drainage systems in turn consist of nine river basins with some bearing names resembling the drainage systems. These nine basins are indicated in Figure 3.1.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
 &lt;br /&gt;
&lt;br /&gt;
Figure 3.1: The River Basins of Tanzania (Source: NWSDS, 2008)&lt;br /&gt;
&lt;br /&gt;
Legend for Figure 3.1&lt;br /&gt;
&lt;br /&gt;
(I) Pangani River Basin	(V) Lakes Nyasa Basin&lt;br /&gt;
(II) Wami/Ruvu River Basin	(VI) Internal Drainage Basin&lt;br /&gt;
(III) Rufiji River Basin	(VII) Lake Rukwa Basin&lt;br /&gt;
(IV) Ruvuma and South Coastal River Basin	(VIII) Lake Tanganyika Basin&lt;br /&gt;
(IX) Lake Victoria Basin&lt;br /&gt;
	&lt;br /&gt;
From geographical point of view, Tanzania is a party to at least eleven transboundary water resources in form of Lakes and Rivers (NWSDS, 2008). These include the following:&lt;br /&gt;
&lt;br /&gt;
•	Lake Victoria,&lt;br /&gt;
•	Lake Tanganyika,&lt;br /&gt;
•	Lake Nyasa,&lt;br /&gt;
•	Lake Chala,&lt;br /&gt;
•	Lake Jipe,&lt;br /&gt;
•	Kagera River,&lt;br /&gt;
•	Mara River,&lt;br /&gt;
•	Pangani River,&lt;br /&gt;
•	Umba River,&lt;br /&gt;
•	Ruvuma River and&lt;br /&gt;
•	Songwe River.&lt;br /&gt;
&lt;br /&gt;
With its numerous water bodies, Tanzania is perceived to have abundant surface and groundwater resources for meeting its present consumptive and non-consumptive needs. However, the reality is that severe and widespread water shortages exist in many areas of Tanzania because of climate variability, poor distribution of the resource in terms of time and space, and inadequate management of the water resources (NWSDS, 2008). As a result, Tanzania experiences frequent and intense water shortages and some water use conflicts.&lt;br /&gt;
&lt;br /&gt;
Furthermore, Tanzania is relatively dry with more than half of the country receiving, on average, less than 800 mm of rainfall per year depending upon air circulation patterns and the movement of the convergence zones in the region. The semi-arid Central and Northern parts of the country, including areas immediately South of Lake Victoria receive less than 700 mm of rainfall per annum and are dry for an average of seven consecutive months a year. River flows in these areas are intermittent. In the Southern, Western and Northern highlands, which receive more than 1,000 mm/year of rainfall, rivers are perennial, and some of these experience frequent floods.&lt;br /&gt;
 &lt;br /&gt;
As an example, in 1999 the availability of renewable freshwater resources, both surface and groundwater was estimated  to be about 2,700 m3/capita/year. By 2018, this estimate was reduced to 2,330 m3/capita/year due to increased population alone.  The average figure is significantly above the level of 1,700 m3/capita/year set by the United Nations as denoting water stress, or 1,000 m3/capita/year denoting water scarcity. Furthermore, due to the projected population growth alone, Tanzania's annual freshwater renewal rate is projected to drop to 1,500 m3/capita/year by 2025, thus categorising the country as being water stressed by then. &lt;br /&gt;
&lt;br /&gt;
On the whole, Tanzania has sufficient surface and ground water resource potential to meet most of her present needs.  However, differences in topography, rainfall patterns and climate account for the existing variation in the availability of water in different parts of the country.  In the densely populated Pangani and Rufiji Basins, these variations have already resulted into water stress.  It is estimated that the annual surface runoff from Tanzania to the world’s oceans is about 74 x 109 m3. The Rufiji, which drains a 177,000 km2 area, contributes over 50% of the runoff3. Typical annual runoffs are shown in the Table 3.1 for some of the major rivers of Tanzania. &lt;br /&gt;
&lt;br /&gt;
Table 3.1 Mean annual river discharges for some of the principal rivers of Tanzania&lt;br /&gt;
River 	Mean Annual Discharge (Million m3/yr) &lt;br /&gt;
Rufiji (at Steiglers Gorge) 	22,250 &lt;br /&gt;
Kilombero (at Swero) 	14,470 &lt;br /&gt;
Malagarasi (at Taragi Ferry) 	5,060 &lt;br /&gt;
Ruvu (at Moro Bridge) 	1,370 &lt;br /&gt;
Wami (at Mandera) 	3,280 &lt;br /&gt;
Ruhuhu (at Kikonge) 	5,600 &lt;br /&gt;
Kiwira (at Kyela) 	1,900 &lt;br /&gt;
Kagera (at Kyaka) 	7,064 &lt;br /&gt;
Mara (at Mara Mines) 	1,971 &lt;br /&gt;
Pangani (at Hale) 	627 &lt;br /&gt;
(Source: NWSDS, 2008)&lt;br /&gt;
 &lt;br /&gt;
&lt;br /&gt;
The most abundant surface water resources exist in Lakes Victoria, Tanganyika, Nyasa, Chala and Jipe, as well as the Kagera, Mara and Songwe rivers, which are trans-boundary waters. The use of these abundant surface water resources for water supply, irrigation and other purposes is still very limited even today.&lt;br /&gt;
&lt;br /&gt;
Tanzania is also rich in wetland systems that are areas which, for part of the year, have enough water to enable the development of types of plants and animals adapted to these conditions.  These include the lakes of the Western and Eastern Rift Valley system, Lake Victoria, numerous small lakes, riverine flood plains and permanent swamps, coastal mangrove and deltaic systems, and a number of artificial impoundments and reservoirs and fish ponds.  There are numerous permanent and seasonal freshwater swamps and flood plains distributed in almost all of the country's major drainage basins, which account for some 2.7 million hectares.  The largest in this category are found in the Rufiji/Ruaha river system and in the Malagarasi/Moyowosi system, while other river systems are the Kagera River, along with Ugalla River, Suiwe River, Mara River, Pangani, Wami and Ruvu Rivers. The principal wetlands of Tanzania constitute one of the country's richest and most durable resources. &lt;br /&gt;
&lt;br /&gt;
3.2	Water Sources Available in Tanzania Mainland&lt;br /&gt;
In Tanzania, there are three main categories of water sources available, namely rainwater, surface and groundwater. &lt;br /&gt;
&lt;br /&gt;
3.2.1	Rainwater and fog harvesting&lt;br /&gt;
One of sources of water include rainwater and fog that can generate limited amounts of very clean water if they are properly collected and stored. In an area where other water sources are not available, consideration should be given to harvesting rainwater and fog.&lt;br /&gt;
&lt;br /&gt;
3.2.2	Surface Water&lt;br /&gt;
For design purposes, the surface water sources that can be considered include;&lt;br /&gt;
•	Rivers or streams,&lt;br /&gt;
•	Impoundments (Reservoirs and ponds),&lt;br /&gt;
•	Springs,&lt;br /&gt;
•	Lakes,&lt;br /&gt;
•	Dams (charco, sand, earth etc).&lt;br /&gt;
&lt;br /&gt;
A brief description of each water source is provided below.&lt;br /&gt;
&lt;br /&gt;
3.2.2.1	 Rivers or streams &lt;br /&gt;
Rivers and streams are water sources that originate from springs located in highlands which flow down to the end of the respective drainage basin which can be lakes, seas or oceans as depicted on the map of Tanzania in Figure 3.1. &lt;br /&gt;
3.2.2.2	 Impoundments&lt;br /&gt;
Impoundments includes all types of reservoirs that emanate from road borrow pits, mining, human or natural activities that are utilised as sources of water for a formal water supply project. &lt;br /&gt;
3.2.2.3	 Springs&lt;br /&gt;
Springs include artesian or freely flowing spring water that has been tapped by an intake structure to facilitate supply of water to a designated community. Spring is a point where groundwater flows out of the ground, and is thus where the aquifer surface meets the ground surface. A spring may be ephemeral (intermittent) or perennial (continuous). Springs can be developed by enlarging the water outlet and constructing an intake structure for water catchment and storage. &lt;br /&gt;
&lt;br /&gt;
3.2.2.4	Lakes &lt;br /&gt;
Lakes found in Tanzania are either located at the end of drainage basins or are highland lakes and some of them are volcanic lakes. Tanzania is endowed with many small inland lakes apart from the third biggest lake in the world (Lake Victoria) as well as Lake Tanganyika which is the world’s deepest lake. Both lakes supply water to various localities around their respective catchments.&lt;br /&gt;
3.2.2.5	 Dams &lt;br /&gt;
Dams are classified based on the availability of construction materials. Various types of dams can be built ranging from earth fill dams, concrete dams, sand dams and charco dams. These are purposely built structures that allow impoundment of river and/or rain water for various end uses. &lt;br /&gt;
&lt;br /&gt;
3.2.3	Groundwater&lt;br /&gt;
Groundwater is that portion of rainwater which has percolated beneath the ground surface to form an underground reservoir referred to as aquifer water. The upper surface of groundwater is the water table. Groundwater is often clear, free from organic matter and bacteria due to the filtering effect of the soil on water percolating through it. However, groundwater almost always contains dissolved minerals from the soil. Groundwater is often better in terms of quality than surface waters. It is less expensive to develop for use, and usually provides more adequate supply in many areas in the country. In semi-arid and the drier parts of the country,  groundwater has played and will continue to play a major role as the sole water source for various uses especially in the central and northern parts of the country and the drier regions of Dodoma, Singida, Shinyanga, Tabora, Mwanza, Mara, Arusha, Coast and Southern Kilimanjaro.&lt;br /&gt;
&lt;br /&gt;
Groundwater can be considered as either spring water or well (or borehole) water. Springs, offer excellent water supply opportunities, but are generally found in hilly or mountainous areas only. They may require long pipelines in order to bring the water to the demand area. This is a feasible source for larger and concentrated settlements but rarely for dispersed populations. For rural water supply systems, groundwater is generally preferred as a water source. &lt;br /&gt;
&lt;br /&gt;
The main sub-types of groundwater and extraction methods are as follows:&lt;br /&gt;
&lt;br /&gt;
3.2.3.1	 Infiltration galleries/wells &lt;br /&gt;
Infiltration galleries are horizontal wells, constructed by digging a trench into the water-bearing sand and installing perforated pipes in it. Water collected in these pipes converges into a “well” from which it is pumped out. &lt;br /&gt;
3.2.3.2	 Well&lt;br /&gt;
This is a hole constructed by any method such as digging, driving, boring, or drilling for the purpose of extracting water from underground aquifers. Wells can vary greatly in depth, water volume and water quality. Well water typically contains more minerals in solution than surface water and may require treatment to soften the water by removing minerals such as arsenic, iron and manganese. Well water may be drawn by pumping from a source below the surface of the earth. Alternatively, it could be drawn up using containers, such as buckets that are raised mechanically or by hand.&lt;br /&gt;
&lt;br /&gt;
Wells are various types of artificially constructed water production wells that are designated as shallow wells (up to 20 metres deep) or deep wells (more than 20 metres deep) as designated by the Ministry responsible for water from time to time.  Water is pumped out of the well into the end user containers or a storage tank using various types of pumps that can be driven manually or using various energies. Typical cross sections through such wells are given in Section 3.6.5.&lt;br /&gt;
3.2.3.3	Classification of wells based on the aquifer tapped&lt;br /&gt;
As mentioned, an aquifer contains a considerable amount of groundwater underground beneath layers of permeable soil material like sand or gravel. Aside from their water storage capacity, aquifers allow the underground flow of groundwater. Aquifers are recharged with rainwater that seeps down to the soil and through the permeable layers.&lt;br /&gt;
3.2.3.3.1	Shallow wells&lt;br /&gt;
Generally, a well is considered shallow if it is less than 20 metres deep. Shallow wells tap the upper water-bearing layer underground. This permeable layer, however, usually has limited safe yield due to its great dependence on seasonal rainfalls. Therefore, the supply capacity of shallow wells could be unreliable and are sometimes intermittent. Also, the water extracted from the upper strata is usually more affected by contamination since the aquifer being tapped is near the ground surface where possible sources of contamination are abound. Protection against contamination is therefore one of the main considerations in constructing a shallow well.&lt;br /&gt;
3.2.3.3.2	Deep wells&lt;br /&gt;
Deep wells, which are over 20 metres deep, tap the deeper unconfined aquifer. This aquifer is not confined by an overlying impermeable layer and is characterized by the presence of a water table. A deep well is less susceptible to surface contamination because of the deeper aquifer. Also, its yield tends to be more reliable since it is less affected by seasonal precipitation.&lt;br /&gt;
&lt;br /&gt;
3.2.3.3.3	Artesian wells&lt;br /&gt;
Artesian wells are much like the deep wells except that the water extracted is from a confined aquifer. The confining impermeable layers are above and below the aquifer. Groundwater recharge enters the aquifer through permeable layers at high elevations causing the confined groundwater at the lower elevations to be under pressure. In some cases, the hydraulic pressure of the aquifer is sufficient for a well to flow freely at the well head.&lt;br /&gt;
&lt;br /&gt;
3.3	Quality Suitability of Water Sources for Water Supply Projects&lt;br /&gt;
When considering the different water sources for water supply projects, it is necessary to ensure that the quality of the water source expected to be utilised is monitored well preferably for a period of not less than three years consecutively to ensure the variability of the quality is captured during the wet and dry seasons. When one looks at the list of the potential sources presented in the foregoing section, such a monitoring programme may not be necessary for rainwater and fog. Only short-term monitoring of the quality of these two sources should be undertaken.&lt;br /&gt;
&lt;br /&gt;
3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment&lt;br /&gt;
&lt;br /&gt;
A decision on whether the water source needs to be subject to water treatment or otherwise will emanate from the results of the short term tests on the quality of the water which will in turn guide the decision of pilot testing the recommended flow sheets particularly for river/streams, lakes, impoundments and dams. Groundwater will usually need only a few unit operations for removal of the identified elevated impurities that may include Iron, Manganese or Fluoride and the need to disinfect water from shallow wells in addition to maintaining residual disinfectants for prevention of re-contamination. Rainwater and condensates from fog will not need to be pilot tested.&lt;br /&gt;
&lt;br /&gt;
3.5	General Considerations for Selection of Water Sources &lt;br /&gt;
In the selection of a source or sources of water supply, adequacy and reliability of the available supply can be considered as the overriding criteria. Without these, the water supply system cannot be considered viable. These, together with the other factors that should be considered (and which are interdependent), are as follows:&lt;br /&gt;
&lt;br /&gt;
3.5.1	Adequacy and reliability&lt;br /&gt;
Adequacy of water supply requires that the quantity of water flow of water source be large enough to meet present and future water demand. On the other hand, source reliability can be expressed by how frequently a water system expects normal demand to go unmet, such as a one-in -25 year or even a one-in-50 year drought. Safe yield is a 1-day low flow rate that is exceeded for 96 percent of the period of record and that can be related to the determined average daily water demand in order to establish the reliability of a water source. For a river/stream, safe yield represents the minimum flow rate that will guarantee no risk to the river hydrology and its surroundings. Safe yield is estimated so as to check whether the planned withdrawal for water supply purposes will be met. To determine the safe yield of a river or stream, a flow -frequency/probability analysis presented in section 3.1.5.5 should be performed. From the analysis, the determined 96 % low flow index should be taken as the safe yield of the river or stream and thus considered as the water source reliability.&lt;br /&gt;
&lt;br /&gt;
3.5.2	Quality of water sources&lt;br /&gt;
The assessment of water quality of a water source is important to establish the suitability of water source for human consumption. The quality of surface water is determined by the amount of pollutants and contaminants picked up by the water in the course of its travel. While flowing over the ground, surface water collects silt, decaying organic matter, bacteria and other micro-organisms from the soil. Sources which require little or no treatment of the water should be chosen in the first instance, provided the required quantity of water can be obtained. Hence springs and ground water resources should always be exploited in the first hand. Surface water from rivers, streams and lakes will almost always require some treatment to render it safe for human consumption. However, for large supplies, surface water will often still be the most economical alternative. Rivers which have the bulk of their catchments in forest areas should be preferred.&lt;br /&gt;
&lt;br /&gt;
Thus, all surface water sources should be presumed to be unsafe for human consumption without some form of treatment. The option to treat surface water to make it safe for human consumption in compliance with the latest edition of Tanzania potable water standards (TBS, TZS 789) has to be evaluated to decide on the feasibility of the water supply project.&lt;br /&gt;
&lt;br /&gt;
3.5.3	Technical Requirements&lt;br /&gt;
The development of the source should be technically feasible, the operation and maintenance requirements for the source abstraction and supply system should be appropriate to the resources available.&lt;br /&gt;
&lt;br /&gt;
3.5.4	Cost implications to develop a water source&lt;br /&gt;
The assessment of investment costs to develop a given water source including operation and maintenance costs has a bearing in the selection of the water source for development. Affordability of investment costs is an important factor to be considered in the selection of the water source.&lt;br /&gt;
&lt;br /&gt;
3.5.5	Protection of water sources&lt;br /&gt;
The location of a water source is a key factor in securing the highest quality water source. In analysing a source location, the design engineer should consider the measures necessary to protect the water source from human excreta, from industrial discharges and from agricultural run-off. In addition, measures to establish and maintain watershed control, physical protection and barriers to contamination have to be considered to ensure sustainable quantity and quality of the raw water.&lt;br /&gt;
&lt;br /&gt;
3.5.6	Legal and management requirements&lt;br /&gt;
Ownership of the land and the legal requirements of obtaining permission to abstract are also factors to consider when selecting a source. Sources on private land may cause access problems.&lt;br /&gt;
&lt;br /&gt;
3.5.7	Distance of water supply source&lt;br /&gt;
The source of the water supply must be situated as near to the demand area as possible. Hence, less length of pipes needs to be installed and thus economical transfer and supply of water. The source(s) nearest to the demand area is usually selected.&lt;br /&gt;
&lt;br /&gt;
3.5.8	Topography of the project area and its surroundings&lt;br /&gt;
The area or land between the source and the area to be served by water supply system should not be highly uneven, i.e., it should not have steep slopes because cost of construction or laying of pipes is very high in such areas.&lt;br /&gt;
&lt;br /&gt;
3.5.9	Elevation of a source of water supply&lt;br /&gt;
The source of water must be on a high elevation than the demand area so as to provide sufficient residual pressure in the water for daily requirements. When the water is available at lower levels, then pumps are used to pressurize water. This requires an excess developmental and operational tasks and costs.&lt;br /&gt;
&lt;br /&gt;
3.6	Determination of water source yield&lt;br /&gt;
Sources which require little or no treatment of raw water such as springs, wells and boreholes should be given the highest selection priority provided their yields are sufficient to meet the water demands of the water supply scheme. For large supplies, surface water will continue to be the most economical alternative water source. In selecting surface water sources, rivers with upland and mostly forested catchments should be given preference. Sub-surface water drawn from a riverbed or river bank can sometimes be a viable alternative in dry areas with only seasonal flows in the river, or in rivers with a high silt load.&lt;br /&gt;
&lt;br /&gt;
Sources from which water can be supplied by a gravity system are particularly more favourable than those which require pumping with significant energy costs. For household and small community water supplies, rainwater harvesting will be the most appropriate in most medium and high potential areas in Tanzania that receive sufficient rains.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
3.6.1	Rainwater and fog harvesting&lt;br /&gt;
3.6.1.1	 Rainwater harvesting&lt;br /&gt;
Rainwater harvesting is a technique of collection and storage of rainwater into natural reservoirs or tanks, or the infiltration of surface water into subsurface aquifers (before it is lost as surface runoff). Types of rainwater harvesting systems are described in the sections below.&lt;br /&gt;
&lt;br /&gt;
3.6.1.1.1	Types of rainwater harvesting&lt;br /&gt;
Two types of rainwater harvesting should be considered:&lt;br /&gt;
&lt;br /&gt;
•	Land catchment,&lt;br /&gt;
•	Roof catchment.&lt;br /&gt;
&lt;br /&gt;
Important data for design of rainwater harvesting systems:&lt;br /&gt;
•	Rainfall data&lt;br /&gt;
•	Catchment/Surface Area &lt;br /&gt;
•	Run-off Coefficient&lt;br /&gt;
&lt;br /&gt;
To accurately estimate the potential rainwater supply from a catchment, reliable rainfall data for a 10-year period is required . The Hydrology Section, Tanzania Meteorology Agency, and Agriculture Departments should be contacted for rainfall data wherever rainwater-harvesting technology is proposed. &lt;br /&gt;
&lt;br /&gt;
The amount of rainfall collected depends on the surfaces where rain falls and the runoff coefficient K of the surface. The runoff coefficient varies with topography, land use, vegetation cover, soil type and moisture content of the soil. In selecting run off coefficients the future characteristics of the water shed are considered. If land use varies within a water shed consider the segments individually and use a weighted coefficient value to determine the total runoff for the watershed. Practically annual rainfall falls during the rainy seasons between October and May.&lt;br /&gt;
&lt;br /&gt;
(i) Run-off Coefficients&lt;br /&gt;
Table 3:2 shows the runoff coefficients for various surfaces. They should be used for calculating the fraction of the rainfall which can be harvested.&lt;br /&gt;
&lt;br /&gt;
Table 3.2: Run-Off Coefficients for Different Surfaces&lt;br /&gt;
SURFACE	RUN-OFF&lt;br /&gt;
COEFFICIENT (K)&lt;br /&gt;
1.	Roof catchments	&lt;br /&gt;
	•	Roof tiles	0.8 to 0.9&lt;br /&gt;
	•	Corrugated sheets	0.7 to 0.9&lt;br /&gt;
2.	Ground surface covering&lt;br /&gt;
	•	Concreted	0.6 to 0.8&lt;br /&gt;
	•	Bitumen, plastic sheeting, butyl rubber	0.8 to 0.9&lt;br /&gt;
	•	Pavement of stone, bricks with open joints	0.5 to 0.6&lt;br /&gt;
	•	Pavement of stone, bricks with tightly cemented joints	0.75-0.85&lt;br /&gt;
3.	Compacted and smoothened soil	0.3 to 0.5&lt;br /&gt;
4. Lawns, sandy soil&lt;br /&gt;
	•	2% slope	0.05-0.10&lt;br /&gt;
	•	2.7% slope	0.10-0.15&lt;br /&gt;
	•	&amp;gt;7%	0.15-0.20&lt;br /&gt;
5. Lawns, heavy soil&lt;br /&gt;
	•	2% Slope	0.13-0.17&lt;br /&gt;
	•	2.7% slope	0.18-0.22&lt;br /&gt;
	•	&amp;gt;7%	0.25-0.35&lt;br /&gt;
6.	•	Uncovered surface, flat terrain	0.3&lt;br /&gt;
	•	Uncovered surface, slope less than 10%	0.0 to 0.4&lt;br /&gt;
	•	Rocky natural catchments	0.2 to 0.5&lt;br /&gt;
&lt;br /&gt;
3.6.1.1.2	Components of rainwater harvesting system&lt;br /&gt;
a) Catchments Area: The catchment of a water harvesting system is the surface which directly receives the rainfall and provides water to the system.&lt;br /&gt;
b) Coarse mesh at the roof to prevent the passage of debris.&lt;br /&gt;
c) Gutters to collect and transport rainwater to the storage tank. Gutters can be semi-circular or rectangular and could be made using:&lt;br /&gt;
&lt;br /&gt;
•	Locally available material such as plain galvanised iron sheet (20 to 22 gauge), folded to required shapes &lt;br /&gt;
•	Semi-circular gutters of PVC material can be readily prepared by cutting those pipes into two equal semi-circular channels.&lt;br /&gt;
•	Bamboo trunks cut vertically in half&lt;br /&gt;
&lt;br /&gt;
The size of the gutter should be according to the flow during the highest intensity rain. It is advisable to make them 10 to 15 per cent oversize.&lt;br /&gt;
&lt;br /&gt;
d) Conduits/pipeline that carry rainwater from the catchment or rooftop area to the harvesting system. Conduits can be of any material like polyvinyl chloride (PVC) or galvanized iron (GI), materials that are commonly available.&lt;br /&gt;
&lt;br /&gt;
e) First Flush pipe to separate first rainwater contaminants namely debris, dirt, and dust.&lt;br /&gt;
&lt;br /&gt;
3.6.1.1.3	Estimation of the yield&lt;br /&gt;
A first estimate of the average yield of a catchments area can be found using the following expression.&lt;br /&gt;
S = K × I × A						(3.1)&lt;br /&gt;
Where: &lt;br /&gt;
S = Yield in m3 / annum &lt;br /&gt;
A = Area of catchment/surface, m2 &lt;br /&gt;
I = Average annual rainfall m/annum &lt;br /&gt;
K = runoff coefficient &lt;br /&gt;
&lt;br /&gt;
Determination of average runoff coefficient for the entire catchment area composed of different surfaces can be calculated as follows:&lt;br /&gt;
 +...					(3.2)&lt;br /&gt;
The required capacity of the collection facility should be calculated using available meteorological data showing the rainfall pattern of the area. However, for rough calculations the storage tank, capacity may be calculated as follows:&lt;br /&gt;
C = D × T × 10-3						(3.3)&lt;br /&gt;
&lt;br /&gt;
Where:&lt;br /&gt;
C = Capacity of tank in m3 &lt;br /&gt;
D = Total water demand in litres / day&lt;br /&gt;
T = Longest dry spell in days&lt;br /&gt;
&lt;br /&gt;
3.6.2	Hydrological Analysis of Surface Waters&lt;br /&gt;
The Design Manual for Water Supply projects is expected to reflect the best concepts on what constitutes the basis for designing a safe, reliable and sustainable water system. Hydrological principles must be taken into consideration during the feasibility and preliminary design stages of the water supply system to ensure that from the outset, design and construction of the system is done right. The design engineer must apply hydrological principles during design of the water system to ensure that the system being designed does not result in exhausted water supply sources and empty reservoirs after construction of the project is completed. If it is recognised from the beginning that there is water deficiency from the source, then the water source should not be considered for development.&lt;br /&gt;
&lt;br /&gt;
The following steps should be followed when undertaking hydrological analysis for the water supply projects:&lt;br /&gt;
&lt;br /&gt;
Step 1: Measurement of the quantity of surface water sources,&lt;br /&gt;
Step 2: Low flow assessment of surface water sources,&lt;br /&gt;
Step 3: Flood flow estimation,&lt;br /&gt;
Step 4: Rainfall analysis,&lt;br /&gt;
Step 5: Water permit application,&lt;br /&gt;
Step 6: Data to support hydrological analysis.&lt;br /&gt;
&lt;br /&gt;
Step 1: Measurement of River Discharge&lt;br /&gt;
In order to assess the amount of water available from the identified surface water source, a discharge measurement must be carried out during both the dry and wet seasons. Measurement of discharge will highlight the production capacity of a water source, the information which is important in the planning of a water system. An estimate of the quantity of water that can be reliably produced by a water source gives the planner a basis to decide for or against its development. For the sources to be considered adequate, they must at least satisfy the average day water demand of the area to be served by a water system. The average daily water demand is calculated from estimated average water requirements for domestic, commercial, industrial, public institutions and livestock. The following methods can be used to measure discharge.&lt;br /&gt;
&lt;br /&gt;
a) Volumetric Method&lt;br /&gt;
This method is appropriate for measuring small quantities of flow from small streams and springs. Flow can be measured by measuring the volume. The equipment required are a stop watch and a bucket or drum of known volume. The method consists of determining the time required to fill the bucket or drum. For more accurate results, the measurement is repeated several times, and the average time of these trials is taken.&lt;br /&gt;
&lt;br /&gt;
b) V-Notch Weir Method&lt;br /&gt;
A weir is an overflow structure built across an open channel for the purpose of measuring the rate of flow. Weirs may be rectangular, trapezoidal or triangular in shape. The triangular or V-Notch Weir is a flow measuring device particularly suited for small flows. The V-Notch Weir often used in flow measurements is the 90° V-Notch that is placed in the middle of the channel and water is allowed to flow over it. The water level in the channel is then measured using a gauging rod. The zero point in the rod should be level with the sill or crest of weir/notch. For a known height of water above the zero in the rod, the flow in cumecs for the 90° V-Notch can be obtained by using the formula:&lt;br /&gt;
&lt;br /&gt;
 							(3.4)&lt;br /&gt;
&lt;br /&gt;
 								(3.5)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
Q = Discharge in m3/sec&lt;br /&gt;
H =Height of Water level above the crest of the weir in meters&lt;br /&gt;
In this case, the discharge coefficient of the weir is approximated to be equal to 0.58.&lt;br /&gt;
&lt;br /&gt;
c) Current meter Measurement&lt;br /&gt;
The current meter is an instrument that is used to measure relatively larger quantities of flow from streams and rivers. The instrument consists of a propeller rotating freely on a well-lubricated shaft. The device is lowered into the water and the rate of revolution of the impeller is directly proportional to the velocity of the water flow. A small magnet is usually built into the shaft of the instrument and a coil detects the passage of the magnet and allows the number of revolutions of the shaft in the given time to be counted. Once the rate of revolution of the impeller is known the water velocity can be calculated using the calibration equation for the instrument, which is expressed as follows:&lt;br /&gt;
&lt;br /&gt;
 									(3.6)&lt;br /&gt;
&lt;br /&gt;
Where, &lt;br /&gt;
V is the water velocity in meters per second&lt;br /&gt;
n is the number of revolutions of the impeller per second&lt;br /&gt;
a, b are constants for the particular instrument.&lt;br /&gt;
&lt;br /&gt;
The discharge measurement using the current meter at the time of measurement, Q,  is  determined by multiplying the velocity of flow and water flow cross-section area.&lt;br /&gt;
&lt;br /&gt;
Step 2: Low flow assessment&lt;br /&gt;
The assessment of low flow magnitudes of streams/rivers or springs in hydrology is important in the planning of a water supply system in view of the fact that it reflects on the water source adequacy and reliability to meet the consumer demand. In low flow hydrology, two questions are asked about a particular river identified to be a water source for a given water supply system:&lt;br /&gt;
&lt;br /&gt;
(i)	Does the river supply a particular water demand at all times?&lt;br /&gt;
(ii)	If not, how much water must be stored in order to meet any deficiency which may arise?&lt;br /&gt;
&lt;br /&gt;
Techniques of flow duration curves, annual minimum flow analyses and annual drought volumes are applied to address the two questions.&lt;br /&gt;
&lt;br /&gt;
a) Flow duration curve&lt;br /&gt;
The flow-duration curve (FDC) is defined as a cumulative frequency curve that shows the percent of time specified discharges were equalled or exceeded during a given period. It combines in one curve the flow characteristics of a stream throughout the range of discharge, without regard to the sequence of occurrence. To prepare a flow-duration curve, the daily, weekly, or monthly flows during a given period are arranged according to magnitude, and then percent of time during which specified flow values are equalled or exceeded are computed. &lt;br /&gt;
&lt;br /&gt;
A flow duration curve once it is prepared, is used to determine the indices of low flow magnitudes; for example, the 96-percentile flow (Q96), is the flow that is exceeded for 96 percent of the period of record. This discharge value is a useful index of low flow that is related to the quantity of water that can be available for water supply in the dry season.&lt;br /&gt;
&lt;br /&gt;
The following steps are followed to construct the FDC:&lt;br /&gt;
&lt;br /&gt;
(i)	Rank the observed stream flows in descending order (from the maximum to the minimum value).&lt;br /&gt;
(ii)	Calculate exceedance probability (P) of each flow as follows:&lt;br /&gt;
&lt;br /&gt;
		 						(3.7)&lt;br /&gt;
&lt;br /&gt;
		Where,&lt;br /&gt;
			P is the probability that a given flow will be equalled or exceeded 			(% of time),&lt;br /&gt;
			m is the ranked position of a given flow value on the list,&lt;br /&gt;
			n is the length of the sample.&lt;br /&gt;
&lt;br /&gt;
(iii)	 A FDC is obtained by plotting each ordered observed streamflow value versus the corresponding calculated exceedance probability.&lt;br /&gt;
(iv)	 Read the indices of low flow magnitudes from the FDC corresponding to 90%, 95% and 99% probabilities of exceeded.&lt;br /&gt;
&lt;br /&gt;
b) Low flow frequency analysis&lt;br /&gt;
The frequency analysis of low river flows is performed by analyzing 1-day or 7-day or 10-day annual minimum flow series obtained by selecting the lowest flow values occurring in each year of record. The set of observed annual minimum flow values recorded at any gauging station is assumed to be a random statistical sample from the population of all possible annual minima at the given site.&lt;br /&gt;
&lt;br /&gt;
The selected set of observed annual minimum flow values is fitted to the Gumbel statistical distribution and then the annual minimum flow magnitudes (QT) corresponding to the design probability of failure (1/T) is then estimated from the Gumbel prediction equation:&lt;br /&gt;
&lt;br /&gt;
 								(3.8)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
QT = Low flow magnitude&lt;br /&gt;
T = Return period of one failure in T years&lt;br /&gt;
  and  = Gumbel Parameters &lt;br /&gt;
KT = Frequency factor, obtained as:&lt;br /&gt;
&lt;br /&gt;
 							       (3.9)&lt;br /&gt;
&lt;br /&gt;
Results from low flow frequency analysis:&lt;br /&gt;
(i)	If the value of QT is large in comparison to QD, the average day water demand, then the river can be considered to be able to supply the demand satisfactorily.&lt;br /&gt;
(ii)	On the other hand if QT is less than or of the same order of magnitude as, QD, ,then the river alone without some form of flow regulation could not be considered satisfactory for supplying the demand. &lt;br /&gt;
&lt;br /&gt;
c) Annual drought volumes Analysis&lt;br /&gt;
On the basis of the results obtained from low flow frequency analysis, in case the annual minimum flow magnitudes (QT) corresponding to the design probability of failure (1/T) is found to be less than QD, demand flow, then storage will be required to meet the established water demand. The required storage is determined by carrying out deficiency/drought Volumes Analysis.&lt;br /&gt;
&lt;br /&gt;
The storage required on a river to meet a specific demand depends on the following factors:&lt;br /&gt;
&lt;br /&gt;
•	Variability of the river flow&lt;br /&gt;
•	Magnitude of the demand&lt;br /&gt;
•	Degree of reliability of meeting the demand&lt;br /&gt;
&lt;br /&gt;
The capacity of the reservoir required to augment the river flow in any year can  be determined from the analysis of the series of annual maximum deficiencies (drought volumes) as follows:&lt;br /&gt;
&lt;br /&gt;
Drought volumes V1, V2, V3,…, Vn are computed from a hydrometric record of the river flow (Qi), with reference to the demand flow (QD), i.e., (Vi = Qi-QD). &lt;br /&gt;
&lt;br /&gt;
The set of observed annual maximum deficiencies at any gauging station is assumed to be a random statistical sample. The annual maximum deficiency (VT) corresponding to the probability of failure (1/T) is estimated from the series of annual maximum deficiencies using a statistical distribution, e.g., Gumbel distribution as illustrated in previous section. The design storage of the reservoir can be made equal to the volume VT corresponding to a risk of one failure in T years. &lt;br /&gt;
&lt;br /&gt;
Step 3: Dependable Rainfall Analysis&lt;br /&gt;
Rainfall analysis is carried out when the need arises to determine dependable rainfall in a given area for the purpose of designing a rainwater harvesting system for domestic use. Frequency analysis of recorded annual rainfall data from a given area, enables the determination of the 90% dependable annual rainfall. This is the value of rainfall magnitude that will be exceeded 90% of the time. In the design of Rainwater Water Harvesting system, catchment (i.e. roof) area and depth of rainfall are important parameters for estimation of optimal storage size. Taking note of the fact that rainfall amounts vary on a year to year basis, the computed rainfall magnitude that is exceeded 90% of the time, is taken as the value of annual rainfall depth that can be expected to occur with some degree of certainty and thus used in the design. The exceedance probability is determined by ranking the observed annual rainfall in ascending order (from the minimum to the maximum value) and then calculating non-exceedance probability (P) as follows:&lt;br /&gt;
&lt;br /&gt;
 								(3.10)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
P is the probability that a given rainfall will be equalled or not exceeded (% of time),&lt;br /&gt;
m is the ranked position of a given rainfall value on the list,&lt;br /&gt;
n is the length of the sample.&lt;br /&gt;
&lt;br /&gt;
The probability of dependable rainfall is obtained by calculating  the value of exceedance probability (1 – P).&lt;br /&gt;
&lt;br /&gt;
Step 4: Flood flow estimation for intakes and small dams' spillways&lt;br /&gt;
The need to estimate flood peaks or design floods arises where it is required to design a spillway of a dam proposed for water storage and also the design of water intake structures. Water intakes and spillway of small dams are designed to accommodate the 100-year flood. &lt;br /&gt;
&lt;br /&gt;
Frequency analysis of observed Annual Maximum streamflow records from a gauging station enables the estimation of flood peaks. The statistical distribution namely the Gumbel distribution or other statistical distribution used in Tanzania such as Pearson type 3, Log-Pearson type 3, Log-Normal and General Extreme Value can be used to carry out frequency analysis in order to determine the magnitude of flood peak of 100-year required for the design. The estimation of design flood peak magnitudes for specified return periods using the Gumbel Distribution is illustrated below.&lt;br /&gt;
&lt;br /&gt;
Prediction equation&lt;br /&gt;
&lt;br /&gt;
 								(3.11)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
QT = Flood peak magnitude&lt;br /&gt;
T = Return period of one failure in T years&lt;br /&gt;
  and  = Gumbel Parameters&lt;br /&gt;
KT = Frequency factor, obtained as:&lt;br /&gt;
&lt;br /&gt;
 							(3.12)&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
Estimation of Gumbel parameters by Method of Moments (MoM)&lt;br /&gt;
&lt;br /&gt;
Mean,  							(3.13)&lt;br /&gt;
Standard deviation,  α						(3.14)		&lt;br /&gt;
&lt;br /&gt;
The mean, μ and Standard Deviation values, σ are computed from observed annual maximum streamflow records. Note that other frequency distributions (Pearson type 3, Log-Pearson type 3, Log-Normal and General Extreme Value) have different expressions for estimating the distribution parameters.&lt;br /&gt;
&lt;br /&gt;
Step 5: Application for water permit&lt;br /&gt;
Water abstraction for water supply from a river or spring requires a permit from the respective water basin office. The planner of the water supply project must apply for the water permit abstraction early in the project design because it can affect the viability of a project. The design engineer must seek the water permit if the project involves a new, replacement, increased withdrawal from a source or an increase in the water system’s physical capacity.&lt;br /&gt;
&lt;br /&gt;
Step 6: Environmental flow considerations&lt;br /&gt;
Environmental flow may be computed in terms of magnitude, timing of low flow in the dry month, duration of low flow in days, frequency of occurrence of the low flow event (return period) and rate of change of low flow over time (m3/day of flow recession). The recommended environmental flow varies for individual rivers and streams and therefore to determine its flow value, a comprehensive Environmental Impact Assessment (EIA) should be conducted and approved by NEMC. Also, there are some guidelines and procedures for environmental flow assessment for specific catchments in Tanzania developed by NEMC. Accordingly, designers need to consult NEMC for environmental flow information in their project areas (https://www.nemc.or.tz/).&lt;br /&gt;
&lt;br /&gt;
Step 7: Data to support hydrological analysis&lt;br /&gt;
Hydrological data is invaluable for planning of water supply systems. For example, water source adequacy and reliability can be determined from analysis of streamflow data which is important hydrological data. Hydrological data expected to be collected by water basin offices in Tanzania to support the planning of water supply systems, specifically to answer questions related to the following:&lt;br /&gt;
&lt;br /&gt;
•	Water availability in terms of quantity and quality&lt;br /&gt;
•	Frequency of occurrence of low flows and flood flows&lt;br /&gt;
•	Variability of flow regime in terms of quantity and quality&lt;br /&gt;
&lt;br /&gt;
Important data to be collected include the following:&lt;br /&gt;
&lt;br /&gt;
(i)	Streamflow – required to quantify available water and estimate flood peaks and low flow magnitudes,&lt;br /&gt;
(ii)	Rainfall – required to determine 90% dependable rainfall,&lt;br /&gt;
(iii)	Sediment - Sediment deposition affects the water carrying capacity of rivers and the useful life of reservoirs. Sediment data is required to determine the useful reservoir capacity and the life span of the reservoir.&lt;br /&gt;
(iv)	 Climate data - (Evaporation, Temperature, Wind speed, sunshine hours, radiation and humidity) – required to estimate water loss from reservoirs.&lt;br /&gt;
&lt;br /&gt;
During the feasibility and preliminary design stage, the design engineer must look for streamflow records from stream gauging stations located at or near water intakes and dam sites to support the design work. In a situation where there are no gauging stations at or near water intakes or dam sites, two options may be considered to get flow data to be used in the design.&lt;br /&gt;
&lt;br /&gt;
Option 1: Transfer data from adjacent or neighbouring drainage areas that have comparable or similar characteristics. The same applies to a situation where rainfall data is missing, rainfall data from adjacent or similar catchments is used to derive flow frequency/probability curves required in the design of water supply system.&lt;br /&gt;
Option 2: Install permanent or temporary gauging stations and start recording flow data at the earliest possible time during the planning steps of the water supply project.&lt;br /&gt;
&lt;br /&gt;
3.7	Other considerations for various water sources&lt;br /&gt;
3.7.1	Water permits Considerations&lt;br /&gt;
During the course of implementation of water supply projects, designers will need to work with the relevant Water Basin Authorities and relevant catchment and sub-catchment committees to ensure all water users with water withdrawal permits are considered during the course of sizing the projects to ensure no developmental constraints are faced as a result of ignoring other users. It will be necessary to consult the updated water permits registers maintained by each Basin Water Board prior to planning expansion of any new water supply project.&lt;br /&gt;
&lt;br /&gt;
3.7.2	Conservation of water sources&lt;br /&gt;
In line with NAWAPO, the protection and conservation of water sources is one of the main duties of all the Basin Water Boards.  Intuitively, for national water resources the MoW also has the responsibility to deal with resolution of all water use conflicts. It will ensure that the WRM Act No.11 of 2009 as well as the associated regulations are fully observed by all parties. Other relevant laws such as those associated with pollution coordinated by other agencies or bodies like the National Environment Management Council (NEMC) are observed with respect to water resources. Where transboundary water resources are involved, the MoW has to ensure the protection roles that are expected of Tanzania are properly fulfilled in line with the relevant international laws, agreements or conventions stated in section 1.1.4.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
3.8	References&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=Chapter_Three:_Water_Sources_Analysis&amp;diff=518</id>
		<title>Chapter Three: Water Sources Analysis</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=Chapter_Three:_Water_Sources_Analysis&amp;diff=518"/>
		<updated>2020-03-31T10:56:42Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;Water source forms one single most important element and is a key to proper function and thus sustainability of any water supply project. Evidence shows that whenever proper water source analysis has not been adequately conducted, most of water supply projects fall into dysfunction. Thus, this chapter presents the analysis of water sources. It includes analysis of both surface and ground water. Further, the chapter gets into 'nitty gritty' of each of this category.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
3.1	Availability of Water Resources in Tanzania Mainland&lt;br /&gt;
Tanzania mainland is endowed with a wide range of water resources that includes the main drainage systems, river basins and natural wetlands that are identified in the next paragraphs. With respect to the drainage systems of water resources in Tanzania mainland, it is divided into five drainage systems that include:&lt;br /&gt;
&lt;br /&gt;
•	The Indian Ocean drainage system,&lt;br /&gt;
•	The Internal drainage system to Lake Eyasi, Natron and Bubu depression,&lt;br /&gt;
•	The Internal drainage systems to Lake Rukwa,&lt;br /&gt;
•	The Atlantic Ocean drainage system through Lake Tanganyika, &lt;br /&gt;
•	The Mediterranean Sea drainage system through Lake Victoria.&lt;br /&gt;
&lt;br /&gt;
The drainage systems in turn consist of nine river basins with some bearing names resembling the drainage systems. These nine basins are indicated in Figure 3.1.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
 &lt;br /&gt;
&lt;br /&gt;
Figure 3.1: The River Basins of Tanzania (Source: NWSDS, 2008)&lt;br /&gt;
&lt;br /&gt;
Legend for Figure 3.1&lt;br /&gt;
&lt;br /&gt;
(I) Pangani River Basin	(V) Lakes Nyasa Basin&lt;br /&gt;
(II) Wami/Ruvu River Basin	(VI) Internal Drainage Basin&lt;br /&gt;
(III) Rufiji River Basin	(VII) Lake Rukwa Basin&lt;br /&gt;
(IV) Ruvuma and South Coastal River Basin	(VIII) Lake Tanganyika Basin&lt;br /&gt;
(IX) Lake Victoria Basin&lt;br /&gt;
	&lt;br /&gt;
From geographical point of view, Tanzania is a party to at least eleven transboundary water resources in form of Lakes and Rivers (NWSDS, 2008). These include the following:&lt;br /&gt;
&lt;br /&gt;
•	Lake Victoria,&lt;br /&gt;
•	Lake Tanganyika,&lt;br /&gt;
•	Lake Nyasa,&lt;br /&gt;
•	Lake Chala,&lt;br /&gt;
•	Lake Jipe,&lt;br /&gt;
•	Kagera River,&lt;br /&gt;
•	Mara River,&lt;br /&gt;
•	Pangani River,&lt;br /&gt;
•	Umba River,&lt;br /&gt;
•	Ruvuma River and&lt;br /&gt;
•	Songwe River.&lt;br /&gt;
&lt;br /&gt;
With its numerous water bodies, Tanzania is perceived to have abundant surface and groundwater resources for meeting its present consumptive and non-consumptive needs. However, the reality is that severe and widespread water shortages exist in many areas of Tanzania because of climate variability, poor distribution of the resource in terms of time and space, and inadequate management of the water resources (NWSDS, 2008). As a result, Tanzania experiences frequent and intense water shortages and some water use conflicts.&lt;br /&gt;
&lt;br /&gt;
Furthermore, Tanzania is relatively dry with more than half of the country receiving, on average, less than 800 mm of rainfall per year depending upon air circulation patterns and the movement of the convergence zones in the region. The semi-arid Central and Northern parts of the country, including areas immediately South of Lake Victoria receive less than 700 mm of rainfall per annum and are dry for an average of seven consecutive months a year. River flows in these areas are intermittent. In the Southern, Western and Northern highlands, which receive more than 1,000 mm/year of rainfall, rivers are perennial, and some of these experience frequent floods.&lt;br /&gt;
 &lt;br /&gt;
As an example, in 1999 the availability of renewable freshwater resources, both surface and groundwater was estimated  to be about 2,700 m3/capita/year. By 2018, this estimate was reduced to 2,330 m3/capita/year due to increased population alone.  The average figure is significantly above the level of 1,700 m3/capita/year set by the United Nations as denoting water stress, or 1,000 m3/capita/year denoting water scarcity. Furthermore, due to the projected population growth alone, Tanzania's annual freshwater renewal rate is projected to drop to 1,500 m3/capita/year by 2025, thus categorising the country as being water stressed by then. &lt;br /&gt;
&lt;br /&gt;
On the whole, Tanzania has sufficient surface and ground water resource potential to meet most of her present needs.  However, differences in topography, rainfall patterns and climate account for the existing variation in the availability of water in different parts of the country.  In the densely populated Pangani and Rufiji Basins, these variations have already resulted into water stress.  It is estimated that the annual surface runoff from Tanzania to the world’s oceans is about 74 x 109 m3. The Rufiji, which drains a 177,000 km2 area, contributes over 50% of the runoff3. Typical annual runoffs are shown in the Table 3.1 for some of the major rivers of Tanzania. &lt;br /&gt;
&lt;br /&gt;
Table 3.1 Mean annual river discharges for some of the principal rivers of Tanzania&lt;br /&gt;
River 	Mean Annual Discharge (Million m3/yr) &lt;br /&gt;
Rufiji (at Steiglers Gorge) 	22,250 &lt;br /&gt;
Kilombero (at Swero) 	14,470 &lt;br /&gt;
Malagarasi (at Taragi Ferry) 	5,060 &lt;br /&gt;
Ruvu (at Moro Bridge) 	1,370 &lt;br /&gt;
Wami (at Mandera) 	3,280 &lt;br /&gt;
Ruhuhu (at Kikonge) 	5,600 &lt;br /&gt;
Kiwira (at Kyela) 	1,900 &lt;br /&gt;
Kagera (at Kyaka) 	7,064 &lt;br /&gt;
Mara (at Mara Mines) 	1,971 &lt;br /&gt;
Pangani (at Hale) 	627 &lt;br /&gt;
(Source: NWSDS, 2008)&lt;br /&gt;
 &lt;br /&gt;
&lt;br /&gt;
The most abundant surface water resources exist in Lakes Victoria, Tanganyika, Nyasa, Chala and Jipe, as well as the Kagera, Mara and Songwe rivers, which are trans-boundary waters. The use of these abundant surface water resources for water supply, irrigation and other purposes is still very limited even today.&lt;br /&gt;
&lt;br /&gt;
Tanzania is also rich in wetland systems that are areas which, for part of the year, have enough water to enable the development of types of plants and animals adapted to these conditions.  These include the lakes of the Western and Eastern Rift Valley system, Lake Victoria, numerous small lakes, riverine flood plains and permanent swamps, coastal mangrove and deltaic systems, and a number of artificial impoundments and reservoirs and fish ponds.  There are numerous permanent and seasonal freshwater swamps and flood plains distributed in almost all of the country's major drainage basins, which account for some 2.7 million hectares.  The largest in this category are found in the Rufiji/Ruaha river system and in the Malagarasi/Moyowosi system, while other river systems are the Kagera River, along with Ugalla River, Suiwe River, Mara River, Pangani, Wami and Ruvu Rivers. The principal wetlands of Tanzania constitute one of the country's richest and most durable resources. &lt;br /&gt;
&lt;br /&gt;
3.2	Water Sources Available in Tanzania Mainland&lt;br /&gt;
In Tanzania, there are three main categories of water sources available, namely rainwater, surface and groundwater. &lt;br /&gt;
&lt;br /&gt;
3.2.1	Rainwater and fog harvesting&lt;br /&gt;
One of sources of water include rainwater and fog that can generate limited amounts of very clean water if they are properly collected and stored. In an area where other water sources are not available, consideration should be given to harvesting rainwater and fog.&lt;br /&gt;
&lt;br /&gt;
3.2.2	Surface Water&lt;br /&gt;
For design purposes, the surface water sources that can be considered include;&lt;br /&gt;
•	Rivers or streams,&lt;br /&gt;
•	Impoundments (Reservoirs and ponds),&lt;br /&gt;
•	Springs,&lt;br /&gt;
•	Lakes,&lt;br /&gt;
•	Dams (charco, sand, earth etc).&lt;br /&gt;
&lt;br /&gt;
A brief description of each water source is provided below.&lt;br /&gt;
&lt;br /&gt;
3.2.2.1	 Rivers or streams &lt;br /&gt;
Rivers and streams are water sources that originate from springs located in highlands which flow down to the end of the respective drainage basin which can be lakes, seas or oceans as depicted on the map of Tanzania in Figure 3.1. &lt;br /&gt;
3.2.2.2	 Impoundments&lt;br /&gt;
Impoundments includes all types of reservoirs that emanate from road borrow pits, mining, human or natural activities that are utilised as sources of water for a formal water supply project. &lt;br /&gt;
3.2.2.3	 Springs&lt;br /&gt;
Springs include artesian or freely flowing spring water that has been tapped by an intake structure to facilitate supply of water to a designated community. Spring is a point where groundwater flows out of the ground, and is thus where the aquifer surface meets the ground surface. A spring may be ephemeral (intermittent) or perennial (continuous). Springs can be developed by enlarging the water outlet and constructing an intake structure for water catchment and storage. &lt;br /&gt;
&lt;br /&gt;
3.2.2.4	Lakes &lt;br /&gt;
Lakes found in Tanzania are either located at the end of drainage basins or are highland lakes and some of them are volcanic lakes. Tanzania is endowed with many small inland lakes apart from the third biggest lake in the world (Lake Victoria) as well as Lake Tanganyika which is the world’s deepest lake. Both lakes supply water to various localities around their respective catchments.&lt;br /&gt;
3.2.2.5	 Dams &lt;br /&gt;
Dams are classified based on the availability of construction materials. Various types of dams can be built ranging from earth fill dams, concrete dams, sand dams and charco dams. These are purposely built structures that allow impoundment of river and/or rain water for various end uses. &lt;br /&gt;
&lt;br /&gt;
3.2.3	Groundwater&lt;br /&gt;
Groundwater is that portion of rainwater which has percolated beneath the ground surface to form an underground reservoir referred to as aquifer water. The upper surface of groundwater is the water table. Groundwater is often clear, free from organic matter and bacteria due to the filtering effect of the soil on water percolating through it. However, groundwater almost always contains dissolved minerals from the soil. Groundwater is often better in terms of quality than surface waters. It is less expensive to develop for use, and usually provides more adequate supply in many areas in the country. In semi-arid and the drier parts of the country,  groundwater has played and will continue to play a major role as the sole water source for various uses especially in the central and northern parts of the country and the drier regions of Dodoma, Singida, Shinyanga, Tabora, Mwanza, Mara, Arusha, Coast and Southern Kilimanjaro.&lt;br /&gt;
&lt;br /&gt;
Groundwater can be considered as either spring water or well (or borehole) water. Springs, offer excellent water supply opportunities, but are generally found in hilly or mountainous areas only. They may require long pipelines in order to bring the water to the demand area. This is a feasible source for larger and concentrated settlements but rarely for dispersed populations. For rural water supply systems, groundwater is generally preferred as a water source. &lt;br /&gt;
&lt;br /&gt;
The main sub-types of groundwater and extraction methods are as follows:&lt;br /&gt;
&lt;br /&gt;
3.2.3.1	 Infiltration galleries/wells &lt;br /&gt;
Infiltration galleries are horizontal wells, constructed by digging a trench into the water-bearing sand and installing perforated pipes in it. Water collected in these pipes converges into a “well” from which it is pumped out. &lt;br /&gt;
3.2.3.2	 Well&lt;br /&gt;
This is a hole constructed by any method such as digging, driving, boring, or drilling for the purpose of extracting water from underground aquifers. Wells can vary greatly in depth, water volume and water quality. Well water typically contains more minerals in solution than surface water and may require treatment to soften the water by removing minerals such as arsenic, iron and manganese. Well water may be drawn by pumping from a source below the surface of the earth. Alternatively, it could be drawn up using containers, such as buckets that are raised mechanically or by hand.&lt;br /&gt;
&lt;br /&gt;
Wells are various types of artificially constructed water production wells that are designated as shallow wells (up to 20 metres deep) or deep wells (more than 20 metres deep) as designated by the Ministry responsible for water from time to time.  Water is pumped out of the well into the end user containers or a storage tank using various types of pumps that can be driven manually or using various energies. Typical cross sections through such wells are given in Section 3.6.5.&lt;br /&gt;
3.2.3.3	Classification of wells based on the aquifer tapped&lt;br /&gt;
As mentioned, an aquifer contains a considerable amount of groundwater underground beneath layers of permeable soil material like sand or gravel. Aside from their water storage capacity, aquifers allow the underground flow of groundwater. Aquifers are recharged with rainwater that seeps down to the soil and through the permeable layers.&lt;br /&gt;
3.2.3.3.1	Shallow wells&lt;br /&gt;
Generally, a well is considered shallow if it is less than 20 metres deep. Shallow wells tap the upper water-bearing layer underground. This permeable layer, however, usually has limited safe yield due to its great dependence on seasonal rainfalls. Therefore, the supply capacity of shallow wells could be unreliable and are sometimes intermittent. Also, the water extracted from the upper strata is usually more affected by contamination since the aquifer being tapped is near the ground surface where possible sources of contamination are abound. Protection against contamination is therefore one of the main considerations in constructing a shallow well.&lt;br /&gt;
3.2.3.3.2	Deep wells&lt;br /&gt;
Deep wells, which are over 20 metres deep, tap the deeper unconfined aquifer. This aquifer is not confined by an overlying impermeable layer and is characterized by the presence of a water table. A deep well is less susceptible to surface contamination because of the deeper aquifer. Also, its yield tends to be more reliable since it is less affected by seasonal precipitation.&lt;br /&gt;
&lt;br /&gt;
3.2.3.3.3	Artesian wells&lt;br /&gt;
Artesian wells are much like the deep wells except that the water extracted is from a confined aquifer. The confining impermeable layers are above and below the aquifer. Groundwater recharge enters the aquifer through permeable layers at high elevations causing the confined groundwater at the lower elevations to be under pressure. In some cases, the hydraulic pressure of the aquifer is sufficient for a well to flow freely at the well head.&lt;br /&gt;
&lt;br /&gt;
3.3	Quality Suitability of Water Sources for Water Supply Projects&lt;br /&gt;
When considering the different water sources for water supply projects, it is necessary to ensure that the quality of the water source expected to be utilised is monitored well preferably for a period of not less than three years consecutively to ensure the variability of the quality is captured during the wet and dry seasons. When one looks at the list of the potential sources presented in the foregoing section, such a monitoring programme may not be necessary for rainwater and fog. Only short-term monitoring of the quality of these two sources should be undertaken.&lt;br /&gt;
&lt;br /&gt;
3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment&lt;br /&gt;
&lt;br /&gt;
A decision on whether the water source needs to be subject to water treatment or otherwise will emanate from the results of the short term tests on the quality of the water which will in turn guide the decision of pilot testing the recommended flow sheets particularly for river/streams, lakes, impoundments and dams. Groundwater will usually need only a few unit operations for removal of the identified elevated impurities that may include Iron, Manganese or Fluoride and the need to disinfect water from shallow wells in addition to maintaining residual disinfectants for prevention of re-contamination. Rainwater and condensates from fog will not need to be pilot tested.&lt;br /&gt;
&lt;br /&gt;
3.5	General Considerations for Selection of Water Sources &lt;br /&gt;
In the selection of a source or sources of water supply, adequacy and reliability of the available supply can be considered as the overriding criteria. Without these, the water supply system cannot be considered viable. These, together with the other factors that should be considered (and which are interdependent), are as follows:&lt;br /&gt;
&lt;br /&gt;
3.5.1	Adequacy and reliability&lt;br /&gt;
Adequacy of water supply requires that the quantity of water flow of water source be large enough to meet present and future water demand. On the other hand, source reliability can be expressed by how frequently a water system expects normal demand to go unmet, such as a one-in -25 year or even a one-in-50 year drought. Safe yield is a 1-day low flow rate that is exceeded for 96 percent of the period of record and that can be related to the determined average daily water demand in order to establish the reliability of a water source. For a river/stream, safe yield represents the minimum flow rate that will guarantee no risk to the river hydrology and its surroundings. Safe yield is estimated so as to check whether the planned withdrawal for water supply purposes will be met. To determine the safe yield of a river or stream, a flow -frequency/probability analysis presented in section 3.1.5.5 should be performed. From the analysis, the determined 96 % low flow index should be taken as the safe yield of the river or stream and thus considered as the water source reliability.&lt;br /&gt;
&lt;br /&gt;
3.5.2	Quality of water sources&lt;br /&gt;
The assessment of water quality of a water source is important to establish the suitability of water source for human consumption. The quality of surface water is determined by the amount of pollutants and contaminants picked up by the water in the course of its travel. While flowing over the ground, surface water collects silt, decaying organic matter, bacteria and other micro-organisms from the soil. Sources which require little or no treatment of the water should be chosen in the first instance, provided the required quantity of water can be obtained. Hence springs and ground water resources should always be exploited in the first hand. Surface water from rivers, streams and lakes will almost always require some treatment to render it safe for human consumption. However, for large supplies, surface water will often still be the most economical alternative. Rivers which have the bulk of their catchments in forest areas should be preferred.&lt;br /&gt;
&lt;br /&gt;
Thus, all surface water sources should be presumed to be unsafe for human consumption without some form of treatment. The option to treat surface water to make it safe for human consumption in compliance with the latest edition of Tanzania potable water standards (TBS, TZS 789) has to be evaluated to decide on the feasibility of the water supply project.&lt;br /&gt;
&lt;br /&gt;
3.5.3	Technical Requirements&lt;br /&gt;
The development of the source should be technically feasible, the operation and maintenance requirements for the source abstraction and supply system should be appropriate to the resources available.&lt;br /&gt;
&lt;br /&gt;
3.5.4	Cost implications to develop a water source&lt;br /&gt;
The assessment of investment costs to develop a given water source including operation and maintenance costs has a bearing in the selection of the water source for development. Affordability of investment costs is an important factor to be considered in the selection of the water source.&lt;br /&gt;
&lt;br /&gt;
3.5.5	Protection of water sources&lt;br /&gt;
The location of a water source is a key factor in securing the highest quality water source. In analysing a source location, the design engineer should consider the measures necessary to protect the water source from human excreta, from industrial discharges and from agricultural run-off. In addition, measures to establish and maintain watershed control, physical protection and barriers to contamination have to be considered to ensure sustainable quantity and quality of the raw water.&lt;br /&gt;
&lt;br /&gt;
3.5.6	Legal and management requirements&lt;br /&gt;
Ownership of the land and the legal requirements of obtaining permission to abstract are also factors to consider when selecting a source. Sources on private land may cause access problems.&lt;br /&gt;
&lt;br /&gt;
3.5.7	Distance of water supply source&lt;br /&gt;
The source of the water supply must be situated as near to the demand area as possible. Hence, less length of pipes needs to be installed and thus economical transfer and supply of water. The source(s) nearest to the demand area is usually selected.&lt;br /&gt;
&lt;br /&gt;
3.5.8	Topography of the project area and its surroundings&lt;br /&gt;
The area or land between the source and the area to be served by water supply system should not be highly uneven, i.e., it should not have steep slopes because cost of construction or laying of pipes is very high in such areas.&lt;br /&gt;
&lt;br /&gt;
3.5.9	Elevation of a source of water supply&lt;br /&gt;
The source of water must be on a high elevation than the demand area so as to provide sufficient residual pressure in the water for daily requirements. When the water is available at lower levels, then pumps are used to pressurize water. This requires an excess developmental and operational tasks and costs.&lt;br /&gt;
&lt;br /&gt;
3.6	Determination of water source yield&lt;br /&gt;
Sources which require little or no treatment of raw water such as springs, wells and boreholes should be given the highest selection priority provided their yields are sufficient to meet the water demands of the water supply scheme. For large supplies, surface water will continue to be the most economical alternative water source. In selecting surface water sources, rivers with upland and mostly forested catchments should be given preference. Sub-surface water drawn from a riverbed or river bank can sometimes be a viable alternative in dry areas with only seasonal flows in the river, or in rivers with a high silt load.&lt;br /&gt;
&lt;br /&gt;
Sources from which water can be supplied by a gravity system are particularly more favourable than those which require pumping with significant energy costs. For household and small community water supplies, rainwater harvesting will be the most appropriate in most medium and high potential areas in Tanzania that receive sufficient rains.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
3.6.1	Rainwater and fog harvesting&lt;br /&gt;
3.6.1.1	 Rainwater harvesting&lt;br /&gt;
Rainwater harvesting is a technique of collection and storage of rainwater into natural reservoirs or tanks, or the infiltration of surface water into subsurface aquifers (before it is lost as surface runoff). Types of rainwater harvesting systems are described in the sections below.&lt;br /&gt;
&lt;br /&gt;
3.6.1.1.1	Types of rainwater harvesting&lt;br /&gt;
Two types of rainwater harvesting should be considered:&lt;br /&gt;
&lt;br /&gt;
•	Land catchment,&lt;br /&gt;
•	Roof catchment.&lt;br /&gt;
&lt;br /&gt;
Important data for design of rainwater harvesting systems:&lt;br /&gt;
•	Rainfall data&lt;br /&gt;
•	Catchment/Surface Area &lt;br /&gt;
•	Run-off Coefficient&lt;br /&gt;
&lt;br /&gt;
To accurately estimate the potential rainwater supply from a catchment, reliable rainfall data for a 10-year period is required . The Hydrology Section, Tanzania Meteorology Agency, and Agriculture Departments should be contacted for rainfall data wherever rainwater-harvesting technology is proposed. &lt;br /&gt;
&lt;br /&gt;
The amount of rainfall collected depends on the surfaces where rain falls and the runoff coefficient K of the surface. The runoff coefficient varies with topography, land use, vegetation cover, soil type and moisture content of the soil. In selecting run off coefficients the future characteristics of the water shed are considered. If land use varies within a water shed consider the segments individually and use a weighted coefficient value to determine the total runoff for the watershed. Practically annual rainfall falls during the rainy seasons between October and May.&lt;br /&gt;
&lt;br /&gt;
(i) Run-off Coefficients&lt;br /&gt;
Table 3:2 shows the runoff coefficients for various surfaces. They should be used for calculating the fraction of the rainfall which can be harvested.&lt;br /&gt;
&lt;br /&gt;
Table 3.2: Run-Off Coefficients for Different Surfaces&lt;br /&gt;
SURFACE	RUN-OFF&lt;br /&gt;
COEFFICIENT (K)&lt;br /&gt;
1.	Roof catchments	&lt;br /&gt;
	•	Roof tiles	0.8 to 0.9&lt;br /&gt;
	•	Corrugated sheets	0.7 to 0.9&lt;br /&gt;
2.	Ground surface covering&lt;br /&gt;
	•	Concreted	0.6 to 0.8&lt;br /&gt;
	•	Bitumen, plastic sheeting, butyl rubber	0.8 to 0.9&lt;br /&gt;
	•	Pavement of stone, bricks with open joints	0.5 to 0.6&lt;br /&gt;
	•	Pavement of stone, bricks with tightly cemented joints	0.75-0.85&lt;br /&gt;
3.	Compacted and smoothened soil	0.3 to 0.5&lt;br /&gt;
4. Lawns, sandy soil&lt;br /&gt;
	•	2% slope	0.05-0.10&lt;br /&gt;
	•	2.7% slope	0.10-0.15&lt;br /&gt;
	•	&amp;gt;7%	0.15-0.20&lt;br /&gt;
5. Lawns, heavy soil&lt;br /&gt;
	•	2% Slope	0.13-0.17&lt;br /&gt;
	•	2.7% slope	0.18-0.22&lt;br /&gt;
	•	&amp;gt;7%	0.25-0.35&lt;br /&gt;
6.	•	Uncovered surface, flat terrain	0.3&lt;br /&gt;
	•	Uncovered surface, slope less than 10%	0.0 to 0.4&lt;br /&gt;
	•	Rocky natural catchments	0.2 to 0.5&lt;br /&gt;
&lt;br /&gt;
3.6.1.1.2	Components of rainwater harvesting system&lt;br /&gt;
a) Catchments Area: The catchment of a water harvesting system is the surface which directly receives the rainfall and provides water to the system.&lt;br /&gt;
b) Coarse mesh at the roof to prevent the passage of debris.&lt;br /&gt;
c) Gutters to collect and transport rainwater to the storage tank. Gutters can be semi-circular or rectangular and could be made using:&lt;br /&gt;
&lt;br /&gt;
•	Locally available material such as plain galvanised iron sheet (20 to 22 gauge), folded to required shapes &lt;br /&gt;
•	Semi-circular gutters of PVC material can be readily prepared by cutting those pipes into two equal semi-circular channels.&lt;br /&gt;
•	Bamboo trunks cut vertically in half&lt;br /&gt;
&lt;br /&gt;
The size of the gutter should be according to the flow during the highest intensity rain. It is advisable to make them 10 to 15 per cent oversize.&lt;br /&gt;
&lt;br /&gt;
d) Conduits/pipeline that carry rainwater from the catchment or rooftop area to the harvesting system. Conduits can be of any material like polyvinyl chloride (PVC) or galvanized iron (GI), materials that are commonly available.&lt;br /&gt;
&lt;br /&gt;
e) First Flush pipe to separate first rainwater contaminants namely debris, dirt, and dust.&lt;br /&gt;
&lt;br /&gt;
3.6.1.1.3	Estimation of the yield&lt;br /&gt;
A first estimate of the average yield of a catchments area can be found using the following expression.&lt;br /&gt;
S = K × I × A						(3.1)&lt;br /&gt;
Where: &lt;br /&gt;
S = Yield in m3 / annum &lt;br /&gt;
A = Area of catchment/surface, m2 &lt;br /&gt;
I = Average annual rainfall m/annum &lt;br /&gt;
K = runoff coefficient &lt;br /&gt;
&lt;br /&gt;
Determination of average runoff coefficient for the entire catchment area composed of different surfaces can be calculated as follows:&lt;br /&gt;
 +...					(3.2)&lt;br /&gt;
The required capacity of the collection facility should be calculated using available meteorological data showing the rainfall pattern of the area. However, for rough calculations the storage tank, capacity may be calculated as follows:&lt;br /&gt;
C = D × T × 10-3						(3.3)&lt;br /&gt;
&lt;br /&gt;
Where:&lt;br /&gt;
C = Capacity of tank in m3 &lt;br /&gt;
D = Total water demand in litres / day&lt;br /&gt;
T = Longest dry spell in days&lt;br /&gt;
&lt;br /&gt;
3.6.2	Hydrological Analysis of Surface Waters&lt;br /&gt;
The Design Manual for Water Supply projects is expected to reflect the best concepts on what constitutes the basis for designing a safe, reliable and sustainable water system. Hydrological principles must be taken into consideration during the feasibility and preliminary design stages of the water supply system to ensure that from the outset, design and construction of the system is done right. The design engineer must apply hydrological principles during design of the water system to ensure that the system being designed does not result in exhausted water supply sources and empty reservoirs after construction of the project is completed. If it is recognised from the beginning that there is water deficiency from the source, then the water source should not be considered for development.&lt;br /&gt;
&lt;br /&gt;
The following steps should be followed when undertaking hydrological analysis for the water supply projects:&lt;br /&gt;
&lt;br /&gt;
Step 1: Measurement of the quantity of surface water sources,&lt;br /&gt;
Step 2: Low flow assessment of surface water sources,&lt;br /&gt;
Step 3: Flood flow estimation,&lt;br /&gt;
Step 4: Rainfall analysis,&lt;br /&gt;
Step 5: Water permit application,&lt;br /&gt;
Step 6: Data to support hydrological analysis.&lt;br /&gt;
&lt;br /&gt;
Step 1: Measurement of River Discharge&lt;br /&gt;
In order to assess the amount of water available from the identified surface water source, a discharge measurement must be carried out during both the dry and wet seasons. Measurement of discharge will highlight the production capacity of a water source, the information which is important in the planning of a water system. An estimate of the quantity of water that can be reliably produced by a water source gives the planner a basis to decide for or against its development. For the sources to be considered adequate, they must at least satisfy the average day water demand of the area to be served by a water system. The average daily water demand is calculated from estimated average water requirements for domestic, commercial, industrial, public institutions and livestock. The following methods can be used to measure discharge.&lt;br /&gt;
&lt;br /&gt;
a) Volumetric Method&lt;br /&gt;
This method is appropriate for measuring small quantities of flow from small streams and springs. Flow can be measured by measuring the volume. The equipment required are a stop watch and a bucket or drum of known volume. The method consists of determining the time required to fill the bucket or drum. For more accurate results, the measurement is repeated several times, and the average time of these trials is taken.&lt;br /&gt;
&lt;br /&gt;
b) V-Notch Weir Method&lt;br /&gt;
A weir is an overflow structure built across an open channel for the purpose of measuring the rate of flow. Weirs may be rectangular, trapezoidal or triangular in shape. The triangular or V-Notch Weir is a flow measuring device particularly suited for small flows. The V-Notch Weir often used in flow measurements is the 90° V-Notch that is placed in the middle of the channel and water is allowed to flow over it. The water level in the channel is then measured using a gauging rod. The zero point in the rod should be level with the sill or crest of weir/notch. For a known height of water above the zero in the rod, the flow in cumecs for the 90° V-Notch can be obtained by using the formula:&lt;br /&gt;
&lt;br /&gt;
 							(3.4)&lt;br /&gt;
&lt;br /&gt;
 								(3.5)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
Q = Discharge in m3/sec&lt;br /&gt;
H =Height of Water level above the crest of the weir in meters&lt;br /&gt;
In this case, the discharge coefficient of the weir is approximated to be equal to 0.58.&lt;br /&gt;
&lt;br /&gt;
c) Current meter Measurement&lt;br /&gt;
The current meter is an instrument that is used to measure relatively larger quantities of flow from streams and rivers. The instrument consists of a propeller rotating freely on a well-lubricated shaft. The device is lowered into the water and the rate of revolution of the impeller is directly proportional to the velocity of the water flow. A small magnet is usually built into the shaft of the instrument and a coil detects the passage of the magnet and allows the number of revolutions of the shaft in the given time to be counted. Once the rate of revolution of the impeller is known the water velocity can be calculated using the calibration equation for the instrument, which is expressed as follows:&lt;br /&gt;
&lt;br /&gt;
 									(3.6)&lt;br /&gt;
&lt;br /&gt;
Where, &lt;br /&gt;
V is the water velocity in meters per second&lt;br /&gt;
n is the number of revolutions of the impeller per second&lt;br /&gt;
a, b are constants for the particular instrument.&lt;br /&gt;
&lt;br /&gt;
The discharge measurement using the current meter at the time of measurement, Q,  is  determined by multiplying the velocity of flow and water flow cross-section area.&lt;br /&gt;
&lt;br /&gt;
Step 2: Low flow assessment&lt;br /&gt;
The assessment of low flow magnitudes of streams/rivers or springs in hydrology is important in the planning of a water supply system in view of the fact that it reflects on the water source adequacy and reliability to meet the consumer demand. In low flow hydrology, two questions are asked about a particular river identified to be a water source for a given water supply system:&lt;br /&gt;
&lt;br /&gt;
(i)	Does the river supply a particular water demand at all times?&lt;br /&gt;
(ii)	If not, how much water must be stored in order to meet any deficiency which may arise?&lt;br /&gt;
&lt;br /&gt;
Techniques of flow duration curves, annual minimum flow analyses and annual drought volumes are applied to address the two questions.&lt;br /&gt;
&lt;br /&gt;
a) Flow duration curve&lt;br /&gt;
The flow-duration curve (FDC) is defined as a cumulative frequency curve that shows the percent of time specified discharges were equalled or exceeded during a given period. It combines in one curve the flow characteristics of a stream throughout the range of discharge, without regard to the sequence of occurrence. To prepare a flow-duration curve, the daily, weekly, or monthly flows during a given period are arranged according to magnitude, and then percent of time during which specified flow values are equalled or exceeded are computed. &lt;br /&gt;
&lt;br /&gt;
A flow duration curve once it is prepared, is used to determine the indices of low flow magnitudes; for example, the 96-percentile flow (Q96), is the flow that is exceeded for 96 percent of the period of record. This discharge value is a useful index of low flow that is related to the quantity of water that can be available for water supply in the dry season.&lt;br /&gt;
&lt;br /&gt;
The following steps are followed to construct the FDC:&lt;br /&gt;
&lt;br /&gt;
(i)	Rank the observed stream flows in descending order (from the maximum to the minimum value).&lt;br /&gt;
(ii)	Calculate exceedance probability (P) of each flow as follows:&lt;br /&gt;
&lt;br /&gt;
		 						(3.7)&lt;br /&gt;
&lt;br /&gt;
		Where,&lt;br /&gt;
			P is the probability that a given flow will be equalled or exceeded 			(% of time),&lt;br /&gt;
			m is the ranked position of a given flow value on the list,&lt;br /&gt;
			n is the length of the sample.&lt;br /&gt;
&lt;br /&gt;
(iii)	 A FDC is obtained by plotting each ordered observed streamflow value versus the corresponding calculated exceedance probability.&lt;br /&gt;
(iv)	 Read the indices of low flow magnitudes from the FDC corresponding to 90%, 95% and 99% probabilities of exceeded.&lt;br /&gt;
&lt;br /&gt;
b) Low flow frequency analysis&lt;br /&gt;
The frequency analysis of low river flows is performed by analyzing 1-day or 7-day or 10-day annual minimum flow series obtained by selecting the lowest flow values occurring in each year of record. The set of observed annual minimum flow values recorded at any gauging station is assumed to be a random statistical sample from the population of all possible annual minima at the given site.&lt;br /&gt;
&lt;br /&gt;
The selected set of observed annual minimum flow values is fitted to the Gumbel statistical distribution and then the annual minimum flow magnitudes (QT) corresponding to the design probability of failure (1/T) is then estimated from the Gumbel prediction equation:&lt;br /&gt;
&lt;br /&gt;
 								(3.8)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
QT = Low flow magnitude&lt;br /&gt;
T = Return period of one failure in T years&lt;br /&gt;
  and  = Gumbel Parameters &lt;br /&gt;
KT = Frequency factor, obtained as:&lt;br /&gt;
&lt;br /&gt;
 							       (3.9)&lt;br /&gt;
&lt;br /&gt;
Results from low flow frequency analysis:&lt;br /&gt;
(i)	If the value of QT is large in comparison to QD, the average day water demand, then the river can be considered to be able to supply the demand satisfactorily.&lt;br /&gt;
(ii)	On the other hand if QT is less than or of the same order of magnitude as, QD, ,then the river alone without some form of flow regulation could not be considered satisfactory for supplying the demand. &lt;br /&gt;
&lt;br /&gt;
c) Annual drought volumes Analysis&lt;br /&gt;
On the basis of the results obtained from low flow frequency analysis, in case the annual minimum flow magnitudes (QT) corresponding to the design probability of failure (1/T) is found to be less than QD, demand flow, then storage will be required to meet the established water demand. The required storage is determined by carrying out deficiency/drought Volumes Analysis.&lt;br /&gt;
&lt;br /&gt;
The storage required on a river to meet a specific demand depends on the following factors:&lt;br /&gt;
&lt;br /&gt;
•	Variability of the river flow&lt;br /&gt;
•	Magnitude of the demand&lt;br /&gt;
•	Degree of reliability of meeting the demand&lt;br /&gt;
&lt;br /&gt;
The capacity of the reservoir required to augment the river flow in any year can  be determined from the analysis of the series of annual maximum deficiencies (drought volumes) as follows:&lt;br /&gt;
&lt;br /&gt;
Drought volumes V1, V2, V3,…, Vn are computed from a hydrometric record of the river flow (Qi), with reference to the demand flow (QD), i.e., (Vi = Qi-QD). &lt;br /&gt;
&lt;br /&gt;
The set of observed annual maximum deficiencies at any gauging station is assumed to be a random statistical sample. The annual maximum deficiency (VT) corresponding to the probability of failure (1/T) is estimated from the series of annual maximum deficiencies using a statistical distribution, e.g., Gumbel distribution as illustrated in previous section. The design storage of the reservoir can be made equal to the volume VT corresponding to a risk of one failure in T years. &lt;br /&gt;
&lt;br /&gt;
Step 3: Dependable Rainfall Analysis&lt;br /&gt;
Rainfall analysis is carried out when the need arises to determine dependable rainfall in a given area for the purpose of designing a rainwater harvesting system for domestic use. Frequency analysis of recorded annual rainfall data from a given area, enables the determination of the 90% dependable annual rainfall. This is the value of rainfall magnitude that will be exceeded 90% of the time. In the design of Rainwater Water Harvesting system, catchment (i.e. roof) area and depth of rainfall are important parameters for estimation of optimal storage size. Taking note of the fact that rainfall amounts vary on a year to year basis, the computed rainfall magnitude that is exceeded 90% of the time, is taken as the value of annual rainfall depth that can be expected to occur with some degree of certainty and thus used in the design. The exceedance probability is determined by ranking the observed annual rainfall in ascending order (from the minimum to the maximum value) and then calculating non-exceedance probability (P) as follows:&lt;br /&gt;
&lt;br /&gt;
 								(3.10)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
P is the probability that a given rainfall will be equalled or not exceeded (% of time),&lt;br /&gt;
m is the ranked position of a given rainfall value on the list,&lt;br /&gt;
n is the length of the sample.&lt;br /&gt;
&lt;br /&gt;
The probability of dependable rainfall is obtained by calculating  the value of exceedance probability (1 – P).&lt;br /&gt;
&lt;br /&gt;
Step 4: Flood flow estimation for intakes and small dams' spillways&lt;br /&gt;
The need to estimate flood peaks or design floods arises where it is required to design a spillway of a dam proposed for water storage and also the design of water intake structures. Water intakes and spillway of small dams are designed to accommodate the 100-year flood. &lt;br /&gt;
&lt;br /&gt;
Frequency analysis of observed Annual Maximum streamflow records from a gauging station enables the estimation of flood peaks. The statistical distribution namely the Gumbel distribution or other statistical distribution used in Tanzania such as Pearson type 3, Log-Pearson type 3, Log-Normal and General Extreme Value can be used to carry out frequency analysis in order to determine the magnitude of flood peak of 100-year required for the design. The estimation of design flood peak magnitudes for specified return periods using the Gumbel Distribution is illustrated below.&lt;br /&gt;
&lt;br /&gt;
Prediction equation&lt;br /&gt;
&lt;br /&gt;
 								(3.11)&lt;br /&gt;
&lt;br /&gt;
Where,&lt;br /&gt;
QT = Flood peak magnitude&lt;br /&gt;
T = Return period of one failure in T years&lt;br /&gt;
  and  = Gumbel Parameters&lt;br /&gt;
KT = Frequency factor, obtained as:&lt;br /&gt;
&lt;br /&gt;
 							(3.12)&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
Estimation of Gumbel parameters by Method of Moments (MoM)&lt;br /&gt;
&lt;br /&gt;
Mean,  							(3.13)&lt;br /&gt;
Standard deviation,  α						(3.14)		&lt;br /&gt;
&lt;br /&gt;
The mean, μ and Standard Deviation values, σ are computed from observed annual maximum streamflow records. Note that other frequency distributions (Pearson type 3, Log-Pearson type 3, Log-Normal and General Extreme Value) have different expressions for estimating the distribution parameters.&lt;br /&gt;
&lt;br /&gt;
Step 5: Application for water permit&lt;br /&gt;
Water abstraction for water supply from a river or spring requires a permit from the respective water basin office. The planner of the water supply project must apply for the water permit abstraction early in the project design because it can affect the viability of a project. The design engineer must seek the water permit if the project involves a new, replacement, increased withdrawal from a source or an increase in the water system’s physical capacity.&lt;br /&gt;
&lt;br /&gt;
Step 6: Environmental flow considerations&lt;br /&gt;
Environmental flow may be computed in terms of magnitude, timing of low flow in the dry month, duration of low flow in days, frequency of occurrence of the low flow event (return period) and rate of change of low flow over time (m3/day of flow recession). The recommended environmental flow varies for individual rivers and streams and therefore to determine its flow value, a comprehensive Environmental Impact Assessment (EIA) should be conducted and approved by NEMC. Also, there are some guidelines and procedures for environmental flow assessment for specific catchments in Tanzania developed by NEMC. Accordingly, designers need to consult NEMC for environmental flow information in their project areas (https://www.nemc.or.tz/).&lt;br /&gt;
&lt;br /&gt;
Step 7: Data to support hydrological analysis&lt;br /&gt;
Hydrological data is invaluable for planning of water supply systems. For example, water source adequacy and reliability can be determined from analysis of streamflow data which is important hydrological data. Hydrological data expected to be collected by water basin offices in Tanzania to support the planning of water supply systems, specifically to answer questions related to the following:&lt;br /&gt;
&lt;br /&gt;
•	Water availability in terms of quantity and quality&lt;br /&gt;
•	Frequency of occurrence of low flows and flood flows&lt;br /&gt;
•	Variability of flow regime in terms of quantity and quality&lt;br /&gt;
&lt;br /&gt;
Important data to be collected include the following:&lt;br /&gt;
&lt;br /&gt;
(i)	Streamflow – required to quantify available water and estimate flood peaks and low flow magnitudes,&lt;br /&gt;
(ii)	Rainfall – required to determine 90% dependable rainfall,&lt;br /&gt;
(iii)	Sediment - Sediment deposition affects the water carrying capacity of rivers and the useful life of reservoirs. Sediment data is required to determine the useful reservoir capacity and the life span of the reservoir.&lt;br /&gt;
(iv)	 Climate data - (Evaporation, Temperature, Wind speed, sunshine hours, radiation and humidity) – required to estimate water loss from reservoirs.&lt;br /&gt;
&lt;br /&gt;
During the feasibility and preliminary design stage, the design engineer must look for streamflow records from stream gauging stations located at or near water intakes and dam sites to support the design work. In a situation where there are no gauging stations at or near water intakes or dam sites, two options may be considered to get flow data to be used in the design.&lt;br /&gt;
&lt;br /&gt;
Option 1: Transfer data from adjacent or neighbouring drainage areas that have comparable or similar characteristics. The same applies to a situation where rainfall data is missing, rainfall data from adjacent or similar catchments is used to derive flow frequency/probability curves required in the design of water supply system.&lt;br /&gt;
Option 2: Install permanent or temporary gauging stations and start recording flow data at the earliest possible time during the planning steps of the water supply project.&lt;br /&gt;
&lt;br /&gt;
3.7	Other considerations for various water sources&lt;br /&gt;
3.7.1	Water permits Considerations&lt;br /&gt;
During the course of implementation of water supply projects, designers will need to work with the relevant Water Basin Authorities and relevant catchment and sub-catchment committees to ensure all water users with water withdrawal permits are considered during the course of sizing the projects to ensure no developmental constraints are faced as a result of ignoring other users. It will be necessary to consult the updated water permits registers maintained by each Basin Water Board prior to planning expansion of any new water supply project.&lt;br /&gt;
&lt;br /&gt;
3.7.2	Conservation of water sources&lt;br /&gt;
In line with NAWAPO, the protection and conservation of water sources is one of the main duties of all the Basin Water Boards.  Intuitively, for national water resources the MoW also has the responsibility to deal with resolution of all water use conflicts. It will ensure that the WRM Act No.11 of 2009 as well as the associated regulations are fully observed by all parties. Other relevant laws such as those associated with pollution coordinated by other agencies or bodies like the National Environment Management Council (NEMC) are observed with respect to water resources. Where transboundary water resources are involved, the MoW has to ensure the protection roles that are expected of Tanzania are properly fulfilled in line with the relevant international laws, agreements or conventions stated in section 1.1.4.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
3.8	References&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=Chapter_Three:_Water_Sources_Analysis&amp;diff=517</id>
		<title>Chapter Three: Water Sources Analysis</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=Chapter_Three:_Water_Sources_Analysis&amp;diff=517"/>
		<updated>2020-03-31T10:55:13Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: Created page with &amp;quot;Water source forms one single most important element and is a key to proper function and thus sustainability of any water supply project. Evidence shows that whenever proper w...&amp;quot;&lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;Water source forms one single most important element and is a key to proper function and thus sustainability of any water supply project. Evidence shows that whenever proper water source analysis has not been adequately conducted, most of water supply projects fall into dysfunction. Thus, this chapter presents the analysis of water sources. It includes analysis of both surface and ground water. Further, the chapter gets into 'nitty gritty' of each of this category.&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=Chapter_Two:_Project_Planning&amp;diff=516</id>
		<title>Chapter Two: Project Planning</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=Chapter_Two:_Project_Planning&amp;diff=516"/>
		<updated>2020-03-31T10:52:41Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;Arguably, planning of water supply projects is considered to be one of the most important stages in the design. Thus, it is strongly advised and emphasized that much time should be spent to undertake proper project planning. A proper project planning will ensure effective and efficient completion of the project successfully. In this chapter, project planning is presented in seven parts that are detailed below. These include:&lt;br /&gt;
&lt;br /&gt;
* Planning considerations for water supply projects&lt;br /&gt;
* Project Planning steps&lt;br /&gt;
* Consulting the Integrated Water Resources Management and Development Plan&lt;br /&gt;
* Consult guideline for preparation of Water Safety Plan – resilient to climate change.&lt;br /&gt;
* Environmental and Social Impact Assessment (ESIA) and Strategic Environmental and Social Impact Assessment (SESIA) Compliance&lt;br /&gt;
* Potential Impacts of Climate Change on Water Supply Projects&lt;br /&gt;
* Participation of CBWSOs in Project Planning Stages&lt;br /&gt;
&lt;br /&gt;
=Chapter Two: Project Planning=&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
==2.1	Planning Considerations for Water Supply Projects ==&lt;br /&gt;
Before commencement of any development of a water project, it is essential to conduct project planning. Planning is a process that should entail the following:&lt;br /&gt;
•	Undertake ESIA and SESIA studies,&lt;br /&gt;
•	Engagement and involvement of the local community to instill the ownership, provide the local knowledge, project buy in and accommodate community needs and requirements,&lt;br /&gt;
•	Assess safe and reliable yield or discharge and quality of water source,&lt;br /&gt;
•	Determination of the system layout,&lt;br /&gt;
•	Conduct design of the water supply project,&lt;br /&gt;
•	Implement the project in terms of construction, operation and maintenance,&lt;br /&gt;
•	Work out to obtain a sound and robust project financing.&lt;br /&gt;
&lt;br /&gt;
It should be emphasized and stressed that collection of good quality, reliable, credible and enough data should be given high priority at all stages of project implementation. Population projection methods and their relevance for rural and urban settings or areas as recommended by the National Bureau of Statistics (NBS) have to be evaluated. Demographic features such as social and economic conditions have to be studied before design projections can be established. Also, water source reliability should be carried out before any further stage of project implementation.&lt;br /&gt;
==2.2	Project Planning Steps==&lt;br /&gt;
Project planning involves a series of steps that determine how project goals will be achieved. The goals may be solicited from the existing community or a strategic plan. In an event that there is not any plan, project plans can be developed through community meetings and gatherings, councils or board meetings, special focused group discussions or other planning processes. &lt;br /&gt;
&lt;br /&gt;
The main steps of project planning include:&lt;br /&gt;
* Step 1: Initiation&lt;br /&gt;
* Step 2: Pre-feasibility study&lt;br /&gt;
* Step 3: Feasibility study&lt;br /&gt;
* Step 4: Preliminary and Detailed Design&lt;br /&gt;
* Step 5: Project phasing&lt;br /&gt;
* Step 6: Procurement&lt;br /&gt;
* Step 7: Implementation/Construction&lt;br /&gt;
* Step 8: Operation and Maintenance (Management)&lt;br /&gt;
* Step 9: Performance Monitoring&lt;br /&gt;
&lt;br /&gt;
The planning of water supply projects can be represented diagrammatically by a step wise planning cycle as shown in Figure 2.1.&lt;br /&gt;
&lt;br /&gt;
==2.3	Pump Protection==&lt;br /&gt;
The following sections provide a brief description of each of the twelve project planning steps.&lt;br /&gt;
&lt;br /&gt;
===2.3.1	Initiation===&lt;br /&gt;
Initiation or sometimes referred to as triggering stage, is a step where initial ideas of the project are presented. Community mobilization through awareness raising is conducted at this stage. The whole idea is to inform the community on the start of the project, solicit community input and knowledge about the project area. Project common understanding is also expected to be realized at this step. &lt;br /&gt;
&lt;br /&gt;
The outcome of this stage of planning is to acquire an understanding of the community conditions and identify problems that prevent the community from achieving its long-range goals. Community conditions which must be collected includes aspects of the community such as: &lt;br /&gt;
* Its geographic location, &lt;br /&gt;
* Demographics, &lt;br /&gt;
* Ecosystem, &lt;br /&gt;
* History,e.t.c&lt;br /&gt;
&lt;br /&gt;
The data collection for the above information should employ community assessment methods.&lt;br /&gt;
&lt;br /&gt;
[[File:Volume I Figure 2.1 Projects Planning Process.png|thumb|Figure 2.1: Projects Planning Process]]&lt;br /&gt;
&lt;br /&gt;
(Source: Modified after Design Manual 3rd edition, 2009)&lt;br /&gt;
 &lt;br /&gt;
====2.3.1.1	Community Assessment Steps====&lt;br /&gt;
* Identify specific community problems that stand in the way of meeting community goals. Produce a community problem statement,&lt;br /&gt;
* Creates a work plan for addressing problems and attaining the goals, &lt;br /&gt;
* Describe measurable beneficial impacts to the community that result from the project’s implementation, &lt;br /&gt;
* Determine the level of resources or funding necessary to implement the project.&lt;br /&gt;
* Solicit community social economic assessment report from Local Government Authorities for use in choice of technology to achieve project sustainability&lt;br /&gt;
&lt;br /&gt;
====2.3.1.2	 Methods of conducting community assessment====&lt;br /&gt;
Two methods can be employed for conducting community assessment. They are comprehensive and strategic planning.&lt;br /&gt;
&lt;br /&gt;
=====2.3.1.2.1	Comprehensive community assessment=====&lt;br /&gt;
This process should involve:&lt;br /&gt;
* Completing a community-wide needs assessment to engage the community in identifying and prioritizing all long-range goals and the community problems preventing the achievement of those goals, &lt;br /&gt;
* Next, the community is involved in the process of developing a method to accomplish long-range goals,  &lt;br /&gt;
* Discussing initial ways to overcome the problems &lt;br /&gt;
* Develop measures to monitor progress towards achieving those goals. &lt;br /&gt;
&lt;br /&gt;
Comprehensive plans require at least a year to complete and should cover a five- to ten-year time span. &lt;br /&gt;
&lt;br /&gt;
======2.3.1.2.2	Strategic community assessment======&lt;br /&gt;
This is a process used when a community or an organization already has a comprehensive plan and wants to move forward to achieve its long-range goals. Strategic planning involves:&lt;br /&gt;
Participation of the community in identifying problems that stand between the community and its goals and to move the community towards realizing its long-range vision. &lt;br /&gt;
&lt;br /&gt;
The product of strategic planning, simply called the “strategic plan,” builds on pre-established long-range goals by designing projects related to one or more of these goals. A strategic plan generally takes at least six months to complete.&lt;br /&gt;
&lt;br /&gt;
===2.3.2	Pre-feasibility Study===&lt;br /&gt;
The pre-feasibility study stage involves initial fieldwork and studies of alternative water resource development plans. The report issued is an outline of possibilities and a list of all the fieldwork activities that need to be accomplished at a feasibility study or even a preliminary engineering design stage.&lt;br /&gt;
&lt;br /&gt;
The objective of this initial study is to determine whether it is worthwhile to proceed with more detailed investigations. In other words at this stage, various projects or alternatives are screened and this should normally reduce the number of options considered feasible to no more than three or so. The report should, however, contain recommendations on the proposed project and how to proceed with the detailed investigations.&lt;br /&gt;
&lt;br /&gt;
These should include indications on the following:&lt;br /&gt;
&lt;br /&gt;
* Data to be collected,&lt;br /&gt;
* Remaining alternatives to be considered and investigated,&lt;br /&gt;
* Professional human resources required,&lt;br /&gt;
* Estimate of time that will be taken or needed,&lt;br /&gt;
* Budgetary financial requirements.&lt;br /&gt;
&lt;br /&gt;
The above are considered taking into account:&lt;br /&gt;
&lt;br /&gt;
* Long term needs,&lt;br /&gt;
* Deficiencies in the existing system (if any),&lt;br /&gt;
* Phases of project implementation.&lt;br /&gt;
&lt;br /&gt;
Briefly, the pre-feasibility report should give an outline of the future development, which seems most appropriate to provide the project area with water in the long term. The other major aim may be to select a short-term project that may be implemented to overcome any immediate needs (crash programme) while the long-term project is being prepared. &lt;br /&gt;
&lt;br /&gt;
===2.3.3	Feasibility Study===&lt;br /&gt;
The feasibility study stage develops the pre-feasibility work further and ends with a Report which normally concentrates on the project alternatives that were recommended for more detailed consideration at the pre-feasibility stage.&lt;br /&gt;
&lt;br /&gt;
The study has to be carried out by a team of competent and experienced personnel from the Ministry, RUWASA and WWSA or with the help of a private sector. At this stage, the following should be achieved:&lt;br /&gt;
&lt;br /&gt;
* Collection of sufficient design data,&lt;br /&gt;
* Appraise the alternatives,&lt;br /&gt;
* Alternative plans (projects) adequately studied and evaluated,&lt;br /&gt;
* Socio-economic analysis adequately conducted and completed&lt;br /&gt;
* Solicit the views and preferences with community in an open meeting&lt;br /&gt;
* Discuss the merits and demerits with community representatives&lt;br /&gt;
* Rank alternatives on the basis of appropriate costing method and perceived ability of community to afford the costs of operation and maintenance and reach agreement in principle with concerned water officials.&lt;br /&gt;
* Inform the community reasons for selection of the alternative(s) and seek their agreement and approval.&lt;br /&gt;
* Conduct Environmental Impact assessment (EIA). For larger projects a statement on Life Cycle Assessment should be included indicating the extent of quantitative and other relevant information currently available,&lt;br /&gt;
* Preliminary engineering design done, including a review of alternative materials,&lt;br /&gt;
* Preliminary cost estimates done,&lt;br /&gt;
* Economic internal rate of return and financial internal rate of return,&lt;br /&gt;
* Carry out design to a level sufficient to enable construction to proceed either using local (District) based contractors or a Force Account approach using local sub-contractors as considered feasible and appropriate,&lt;br /&gt;
* Most feasible project (least cost) selected, &lt;br /&gt;
* Feasibility report prepared and presented to the authorities for approval&lt;br /&gt;
&lt;br /&gt;
The report may also include interim progress reports, appendices of data collected during the detailed study. The feasibility report should be presented as a supporting document to apply for financing from the financing agencies.&lt;br /&gt;
====2.3.3.1	 Water Supply Projects Ranking and Technology Selection Criteria====&lt;br /&gt;
=====2.3.3.1.1	Ranking of Projects=====&lt;br /&gt;
Projects to be implemented should be ranked on the basis of the following criteria;&lt;br /&gt;
* Type of technology,&lt;br /&gt;
* Quantity of water,&lt;br /&gt;
* ESIA Report comments,&lt;br /&gt;
* Negative environment impact,&lt;br /&gt;
* Quality of water available,&lt;br /&gt;
* Cost/benefit analysis, &lt;br /&gt;
* Walking distance scheme complexity.&lt;br /&gt;
&lt;br /&gt;
=====2.3.3.1.2	Choice of Technology=====&lt;br /&gt;
As far as possible ranking of project selection is concerned, technology choice should be based on progressive consideration of:&lt;br /&gt;
* Hand pump(s) from proven permanent deep hand dug well(s) or shallow borehole(s),&lt;br /&gt;
* Gravity scheme from protected spring,&lt;br /&gt;
* Medium or deep well with appropriate hand pump (rotary type),&lt;br /&gt;
* Pumped / Piped Scheme Electrical Driven,&lt;br /&gt;
* Pumped/Piped Scheme Solar Driven.&lt;br /&gt;
&lt;br /&gt;
For point water sources or simple distribution systems, a prime location for a domestic point should be the village primary school followed by a village health facility (if any). Provision of improved sanitation and hand washing facilities at both primary school and health facility should also receive priority consideration in any village scheme. Use the relevant WASH guidelines for design of the washing facilities.&lt;br /&gt;
&lt;br /&gt;
===2.3.4	Preliminary and Detailed Design===&lt;br /&gt;
After the feasibility report is presented and approved, the preliminary and the preferred alternative should be selected and the finances sought. The following should be considered while conducting the design:&lt;br /&gt;
* The Engineer should prepare the preliminary engineering design and then the detailed or final project report,  &lt;br /&gt;
* These reports should provide the basis for implementation,  &lt;br /&gt;
* The initial report has to provide the design basics which are then developed further in the detailed design of the project including working drawings and tender documents,  &lt;br /&gt;
* They should however include a review of all relevant aspects of this DCOM Manual and either accept or otherwise indicate, complete with detailed reasoning, why different criteria is proposed. &lt;br /&gt;
&lt;br /&gt;
In addition, the report should address the following:&lt;br /&gt;
* The issue of costing being adopted and requirement for extent of whole life cycle analysis and adaptation of costing,  &lt;br /&gt;
* Consideration of the environmental impacts of the project and its envisaged elements,  &lt;br /&gt;
* Issue of climate change and its possible effects on the project being designed. &lt;br /&gt;
&lt;br /&gt;
It should be noted that the conceptual designs provided at the feasibility study or preliminary engineering stages are generally inadequate for the construction of the project. Foremost, the Engineer arranges for any outstanding detailed field investigations, surveys and data collection. Based on the detailed field data collected; detailed designs, plans and estimates are prepared.&lt;br /&gt;
&lt;br /&gt;
Detailed designs should include:&lt;br /&gt;
* Statistical analysis of data collected for the population and demand projections; hydrological ,hydrogeological  and meteorological data,&lt;br /&gt;
* Least cost lay-outs for different components of the project, i.e. treatment plants, hydraulic and structural works,&lt;br /&gt;
* Structural and stability computations of different structures,&lt;br /&gt;
* Calculations for pumps, motors, power generators and other machinery and equipment,&lt;br /&gt;
* Engineering analysis for deciding the most economic size of delivery mains.&lt;br /&gt;
* Hydraulic computations for the distribution system,&lt;br /&gt;
* Bills of quantities.&lt;br /&gt;
* Detailed design should include the following:&lt;br /&gt;
&lt;br /&gt;
====2.3.4.1	Detailed Engineering Drawings====&lt;br /&gt;
These should include:&lt;br /&gt;
&lt;br /&gt;
* Index plan showing overall layout of the project,&lt;br /&gt;
* Schematic diagram showing levels of salient components of the project (may not necessarily be to scale),&lt;br /&gt;
* Detailed plans and sections in scale for the headwords, treatment plants, clear water storage tank, pumping station, in a scale 1:20 to 1:100 depending on the details and size of the works,&lt;br /&gt;
* Detailed structural plans for structures, intake, treatment plant, clear water reservoir etc., in a scale of 1:20,&lt;br /&gt;
* Index plan of the distribution system normally in an appropriate scale,&lt;br /&gt;
* Longitudinal sections of the delivery main and details of appurtenances in scales: Horizontal scale 1:500 to 1:5000 depending on distance and details Vertical scale 1:20 to 1:100 depending on the terrain surface undulations.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.2		Detailed estimates of capital costs====&lt;br /&gt;
Project cost estimates should be based on unit costs derived from recent projects of a similar magnitude, complexity and remoteness from or proximity to ports or major urban areas.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.3	 Detailed estimates of recurrent costs====&lt;br /&gt;
As far as possible this should be based on unit costs provided by the operating authority or from schemes of a similar size and nature.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.4	 Anticipated revenue====&lt;br /&gt;
These should be based on the recommendations made regarding tariff structures or provided by the operating authority or regulator.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.5	 Detailed design report====&lt;br /&gt;
A report should accompany the detailed designs, plans and estimates elaborating on the:&lt;br /&gt;
* Engineering aspects,&lt;br /&gt;
* Financial aspects,&lt;br /&gt;
* Administrative aspects, &lt;br /&gt;
* Tender documents &lt;br /&gt;
* Specifications.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.6	 Project write-up to be submitted to potential financiers====&lt;br /&gt;
Each Development Partner may have a different pattern of project presentation for financial request. The project document should therefore follow more guidelines as indicated by the financiers or the local funding sources where applicable.&lt;br /&gt;
&lt;br /&gt;
====2.3.5	Project Phasing====&lt;br /&gt;
Sometimes the implementation of a project is carried out in phases due to among other things, the following reasons:&lt;br /&gt;
* Financial resources available,&lt;br /&gt;
* Opportunity cost of money,&lt;br /&gt;
* Economies of scale,&lt;br /&gt;
* Growth rate in the area,&lt;br /&gt;
* Rate of development in the area,&lt;br /&gt;
* The design (working) life of various installations,&lt;br /&gt;
* Development in levels of service,&lt;br /&gt;
* New technology or method that needs piloting before rolling it out&lt;br /&gt;
Once the basic design period is decided (usually between 10 and 20 years) and water demand is computed for different years, the different elements can be phased. Exceptions do occur where financial assistance capital is being used and there is fear or a probability that further trunches will not be available just a few years later.&lt;br /&gt;
&lt;br /&gt;
Generally, phasing should be undertaken as follows: &lt;br /&gt;
(i)	Dams, river and spring intakes, should be implemented in a single phase to cover all of the ultimate design demand or the hydrologically calculated water availability. This is particularly significant for dams as flood spillways form an expensive integral part and the need to raise a spillway inlet and deal with the additional energy at its exit is usually very costly.&lt;br /&gt;
(ii)	Boreholes to be constructed in Multiple Phases according to the growth in demand.&lt;br /&gt;
(iii)	Treatment plants and storage tanks to be constructed stepwise or in phases, according to the projected growth in demand.&lt;br /&gt;
(iv)	Mechanical installations to be implemented in Multiple Phases according to the design life of the equipment.&lt;br /&gt;
(v)	Pump houses constructed in a Single Phase with space for additional mechanical plant.&lt;br /&gt;
(vi)	Rising mains and main conduits between units to be constructed to cover the ultimate demand in a single Phase.&lt;br /&gt;
(vii)	Long transmission mains to be constructed as two parallel lines in a single Phase where funds allow or in Two Phases where not. It can be advantageous to dedicate one of two parallel transmission mains to supplying water to the terminal reservoir whilst using the second for a mix of local distribution (daytime) and conveyance to the terminal reservoir (night time).&lt;br /&gt;
(viii)	Distribution systems to be constructed according to the growth in development in Multiple Phases.&lt;br /&gt;
&lt;br /&gt;
===2.3.6	Procurement===&lt;br /&gt;
====2.3.6.1	Preparation of Tender Documents====&lt;br /&gt;
The Procurement Management Unit (PMU) using the approved templates as guided by PPRA documentation undertakes preparation of tender documents. In preparing the tender documents undertaken by PMU, unit rate contract is normally adopted for project components such as intake, delivery mains, distribution system, storage tanks and other appurtenances. For specialized areas like the treatment plants and pumping stations it may be necessary to prepare separate tenders for the supply and installation of such facilities. The superstructure may still be included in the main contract bill of quantities. As much as possible one contract is preferred. The suppliers of such specialized equipment would then be included as sub-contractors of the main contractor. Important documents included in contract documents includes:&lt;br /&gt;
* Letter of Invitation to Tender &lt;br /&gt;
* Instruction to Tenderers &lt;br /&gt;
* General Conditions of Contract&lt;br /&gt;
* Special Conditions of Contract&lt;br /&gt;
* Drawings &lt;br /&gt;
* Specifications &lt;br /&gt;
* Bills of Quantities&lt;br /&gt;
* Tender Forms&lt;br /&gt;
* Security Forms &lt;br /&gt;
* Anti-bribery Pledge&lt;br /&gt;
* Schedule of Additional Information&lt;br /&gt;
* Information Data&lt;br /&gt;
&lt;br /&gt;
====2.3.6.2	Tendering process====&lt;br /&gt;
This process involves use of public procurement act to select service providers as detailed in following steps; &lt;br /&gt;
* Issue of tender documents&lt;br /&gt;
* Submission and receipt of tenders&lt;br /&gt;
* Opening of tenders&lt;br /&gt;
* Evaluation of tenders&lt;br /&gt;
* Award of tender&lt;br /&gt;
* Signing of contract agreement&lt;br /&gt;
&lt;br /&gt;
===2.3.7	Implementation/Construction Stage===&lt;br /&gt;
Construction stage includes contract management, Contract supervision and administration.&lt;br /&gt;
====2.3.7.1	Contract Management====&lt;br /&gt;
Contract management entails the following;&lt;br /&gt;
* Contract Management Plan (CMP),&lt;br /&gt;
* Contract Delivery Follow-up,&lt;br /&gt;
* Work progress monitoring &amp;amp; control,  &lt;br /&gt;
* All projects executed must have a completion report (as constructed built reports and drawings). It is essential that Engineers or Foremen keep an up to date record of all project activities including all changes to the original design with reasons for this clearly indicated as well as the approving authority.&lt;br /&gt;
* Initial and Final Acceptance of the Works&lt;br /&gt;
* Contract Close Out&lt;br /&gt;
====2.3.7.2	Contract supervision and administration ====&lt;br /&gt;
During construction stage, it is necessary to consider the following;&lt;br /&gt;
* Each phase of the project implementation should be planned in detail using techniques such as the Critical Path Method (CPM) or Programme Evaluation or/and Review Technique (PERT ) to ensure time control,&lt;br /&gt;
* Work together with the Contractor to prepare a Quality Assurance Plan which shall narrate the scope of the works and the expected quality requirements for the project, the role of the participants in ensuring quality requirements are met&lt;br /&gt;
* Obtain a cash flow forecast from the contractor, and make the Client aware of his payment obligations based on the forecast&lt;br /&gt;
* Keep a close track of all contractors approved claims and adjust the contract price to reflect increase or decrease in the contract price&lt;br /&gt;
* Detailed information in procurement, contract management, contract supervision and administration is detailed well in chapter three and four of Volume III Construction Supervision for Water Supply and Sanitation Projects.&lt;br /&gt;
&lt;br /&gt;
===2.3.8	Operation and Maintenance Stage===&lt;br /&gt;
   This process takes over after the project completion, it involves;&lt;br /&gt;
* Preparation of O&amp;amp;M Plan,&lt;br /&gt;
* Development of Individual Unit Plans for O&amp;amp;M,&lt;br /&gt;
* Plan for capacity Building of O&amp;amp;M Personnel,&lt;br /&gt;
* Plan for Providing Spares and Tools,&lt;br /&gt;
* Plan for Water Audit and Leakage Control,&lt;br /&gt;
* Plan for Efficient Use of Power,&lt;br /&gt;
* Plan for sound financial management system,&lt;br /&gt;
* Plan for Information Education Communication for Water and Sanitation Services,&lt;br /&gt;
* Reports and Record Keeping,&lt;br /&gt;
* Develop appropriate maintenance schedule and check lists,&lt;br /&gt;
* Utilize Standard Operating Procedures,&lt;br /&gt;
* Utilize Water Safety Plans.&lt;br /&gt;
&lt;br /&gt;
Detailed information on planning for operation and maintenance is found in chapter three and four of Volume IV Operation and Maintenance of Water Supply and Sanitation Projects&lt;br /&gt;
&lt;br /&gt;
===2.3.9	Performance Monitoring===&lt;br /&gt;
The aim of the project is to provide the services uninterrupted. To ensure this, a proper monitoring mechanism of the performance of the project should be prepared. Such a mechanism could include proper procedures for procurement and distribution of spare parts, fuel, replacement, a maintenance programme for the project including personnel at the village, District and if necessary at Regional and National levels also. Likewise a water quality surveillance procedure should be instituted in the framework of the existing mechanism.&lt;br /&gt;
&lt;br /&gt;
==2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans==&lt;br /&gt;
It is imperative that during planning of the water supply and sanitation project, designer should consult the Integrated Water Resources Management and Development (IWRMD) plan for a basin where the project is planned to be executed. The development of an IWRMD Plan is a key objective of the water resources component of the Water Sector Development Programme 2006-2025. It is a legal requirement provided for in the Water Resources Management Act, No. 11 of 2009. The plan provides a blueprint for sustainable development and management of the basin’s water resources. &lt;br /&gt;
&lt;br /&gt;
Thus, a water supply and sanitation project designer is advised and encouraged to consult IWRMD plans as they provide:&lt;br /&gt;
&lt;br /&gt;
* The status of water resource availability (both quantity and quality) in the basin,&lt;br /&gt;
* Water data and information necessary for the design of the projects,&lt;br /&gt;
* Framework for water allocations among its competing demands,&lt;br /&gt;
* Water demand for water related sectors,&lt;br /&gt;
* Stakeholders consultation plan.&lt;br /&gt;
&lt;br /&gt;
===2.4.1	Status of Development and Implementation of IWRMD Plans===&lt;br /&gt;
By the time of development of this DCOM manual, IWRMD plans had been developed for six (6) out of the nine basins. The six basins are:&lt;br /&gt;
* Rufiji River Basin,&lt;br /&gt;
* Ruvuma and Southern Coast Basin,&lt;br /&gt;
* Lake Tanganyika Basin,&lt;br /&gt;
* Lake Nyasa Basin,&lt;br /&gt;
* Internal Drainage and&lt;br /&gt;
* Lake Rukwa Basin&lt;br /&gt;
&lt;br /&gt;
It was reported that the development of IWRMD plans for Lake Victoria Basin and Wami/Ruvu basins were on-going. &lt;br /&gt;
&lt;br /&gt;
IWRMD plans implementation challenges have been observed in some basins. These include:&lt;br /&gt;
&lt;br /&gt;
* Inadequate funding to implement plans recommendations,&lt;br /&gt;
* Some plans are not implementable because of including unrealistic recommendations,&lt;br /&gt;
* Some plans are considered to have been more of studies rather than plans,&lt;br /&gt;
* Inadequate human resources capacity to implement them,&lt;br /&gt;
* As required by EMA, ESIAs have not been conducted, contrary to the requirement&lt;br /&gt;
&lt;br /&gt;
===2.4.2	Components of IWRMD Plans===&lt;br /&gt;
The developed IWRMD plans are expected to have the following main components:&lt;br /&gt;
* Component 1: Inventory and review of water availability, use and demand,&lt;br /&gt;
* Component 2: Institutional, Policy and legal framework,&lt;br /&gt;
* Component 3: Sector/Thematic Water Plans,&lt;br /&gt;
* Component 4: Integrated Water Resources Management and Development Plan, &lt;br /&gt;
* Component 5: IWRMD Plan Implementation Strategy and Action Plan.&lt;br /&gt;
&lt;br /&gt;
The production capacity of a source is very important in planning a water supply system. An estimate of the water that can be reliably produced by a water source like a well or spring gives the planner a basis to decide for or against its development. For the source(s) to be considered adequate, they must at least satisfy the maximum daily demand of the area to be served.&lt;br /&gt;
&lt;br /&gt;
==2.5		Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change ==&lt;br /&gt;
&lt;br /&gt;
Water Safety Plan (WSP) is the most effective means of consistently ensuring the safety of a drinking-water supply through the use of a comprehensive risk assessment and risk management approach that encompasses all steps in water supply from the catchment to the consumer (WHO, 2017). The approach enables the operators and managers of water utilities to know the system thoroughly, identify where and how problems could arise, put multiple barriers and management systems in place to stop the problems before they happen and making all parts of the system work properly so as to ensure the safety and acceptability of a drinking water supply intended for human consumption and other domestic uses as summarized in the WHO safe water chain frameworks.&lt;br /&gt;
&lt;br /&gt;
Thus, during the planning phase, a designer should consult guidelines for the preparation of Water Safety Plans - Resilient to Climate Change, which has been prepared and published by Ministry of Water (MoW, 2015)&lt;br /&gt;
&lt;br /&gt;
==2.6	Environmental and Social Impact Assessment Compliance==&lt;br /&gt;
Section 81 of the Environmental Management Act (Cap 191) requires all developers of projects identified in the 3rd Schedule of the Act and detailed in the 1st Schedule of the Environmental Management (Environmental Impact Assessment And Audit) (Amendment) Regulations, 2018, to undertake Environmental Impact Assessment (EIA). Section 82 of EMA (Cap 181) requires that the EIA be carried out prior to the commencement or financing of the project. Procedures for carrying out the EIA, identified under the EIA and Audit  (Amendment) Regulations of 2018 identify eight steps to be followed. According to EIA and Audit (Amendment) Regulations of 2018, projects are classified into the following categories, namely:&lt;br /&gt;
&lt;br /&gt;
(a) “A” category for Mandatory projects;&lt;br /&gt;
 (b) “B1” category for Borderline Project;&lt;br /&gt;
(c) “B2” category for Non-Mandatory; and&lt;br /&gt;
(d) “Special Category&lt;br /&gt;
&lt;br /&gt;
So it is imperative that a proponent and developer of any water supply and sanitation project categorizes their project prior to actual project implementation for the same.&lt;br /&gt;
&lt;br /&gt;
===2.6.1	Procedures for Conducting ESIA in Tanzania===&lt;br /&gt;
Procedures for carrying out the ESIA, identified under the EIA and Audit (Amendment) Regulations of 2018 identify eight key steps to be followed in the EIA process in Tanzania. These are:&lt;br /&gt;
&lt;br /&gt;
* Step 1: Registration,&lt;br /&gt;
* Step 2: Screening, &lt;br /&gt;
* Step 3: Scoping,&lt;br /&gt;
* Step 4: Environmental Assessment,&lt;br /&gt;
* Step 5: Review,&lt;br /&gt;
* Step 6: Recommendations of the Technical Advisory Committee (TAC),&lt;br /&gt;
* Step 7: Submission To The Minister For Environment,&lt;br /&gt;
* Step 8: Approval of the EIS.&lt;br /&gt;
&lt;br /&gt;
It is recommended to consult NEMC guidelines and Environmental Management (Environmental Impact Assessment And Audit) (Amendment) Regulations, 2018 for more details. Also, the following Ministry of Water guidelines, accessible at have to be consulted.&lt;br /&gt;
a)	Guidelines of Good Environmental and Social Practices (GGESP) of July 2019,&lt;br /&gt;
b)	Environmental and Social Management Framework (ESMF) of July 2019.&lt;br /&gt;
&lt;br /&gt;
===2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance===&lt;br /&gt;
&lt;br /&gt;
Section 105 part (2) of the Environmental Act requires that wherever there is a major water project planned for construction, the Ministry responsible for water should conduct Strategic Environmental and Social Assessment. The strategic environmental assessment shall asses the area marked for development and include:&lt;br /&gt;
&lt;br /&gt;
* Baseline environmental conditions and status of natural resources,&lt;br /&gt;
* Identification of ecological sensitive and protected areas,&lt;br /&gt;
* Identification and description of communities around the area,&lt;br /&gt;
* Existing social-economic conditions,&lt;br /&gt;
* Existing economic activities and infrastructure.&lt;br /&gt;
The strategic environmental and social assessment shall be submitted to the Minister responsible for Environment for approval before the planning process.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
==2.7	Potential Impacts of Climate Change on Water Supply Projects==&lt;br /&gt;
It should be emphasized that immediately the project is conceived, hydrological, rainfall and other meteorological data collection must be initiated. In addition and given the long design life of such structures, consideration must be given to the possible impacts of climate change. Detailed account of predictions and impacts of climate change on water supply projects is provided in Appendix A.&lt;br /&gt;
&lt;br /&gt;
URT (2019) has recommended strategies and plans to adapt risks from climate change. The design related strategies of infrastructure, which a designer should consider while planning for water supply projects include:&lt;br /&gt;
&lt;br /&gt;
* Where possible, have at least two sources of supply at different locations. Build superstructures above high flood-line level.&lt;br /&gt;
* Adopt energy-efficiency programmes and, where possible, select facilities which require less power consumption.&lt;br /&gt;
* Monitor wells near coastlines to prevent salinization. If climate change causes sea levels to rise dramatically, even aquifers that have been sustainably utilized can suffer salinization.&lt;br /&gt;
* Utilize renewable energy sources.&lt;br /&gt;
&lt;br /&gt;
Guidelines for resiliency to climate change for urban water supply utilities have been published by the Ministry of Water. &lt;br /&gt;
&lt;br /&gt;
==2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages==&lt;br /&gt;
As explained in detail in section 2.1 of this volume, the CBWSOs have to  be involved in the complete life cycle of the project including ensuring their sustainability during operation and maintenance of the projects under the overall coordination of WSSAs and RUWASA.&lt;br /&gt;
&lt;br /&gt;
==2.9	References==&lt;br /&gt;
Asadieh, B. and Krakauer, N.Y. (2016). Impacts of changes in precipitation amount and distribution on water resources studied using a model rainwater harvesting system. J. Am. Water Resour. Assoc. 52: 1450–1471.https://doi.org/10.1111/ 1752-1688.12472.&lt;br /&gt;
&lt;br /&gt;
Gebrechorkos, S. H., Hülsmann, S., &amp;amp; Bernhofer, C. (2019). Regional climate projections for impact assessment studies in East Africa. Environmental Research Letters, 14(4), 044031. https://doi.org/10.1088/1748-9326/ab055a&lt;br /&gt;
&lt;br /&gt;
Giannini, A., M. Biasutti, I. Held, and A. Sobel (2008). A global perspective on African climate. Clim. Change, 90: 359–383.&lt;br /&gt;
&lt;br /&gt;
Hansingo, K., and C. Reason (2008). Modelling the atmospheric response to SST dipole patterns in the South Indian Ocean with a regional climate model. Meteorol. Atmos. Phys., 100: 37–52.&lt;br /&gt;
&lt;br /&gt;
Hansingo, K., and C. Reason (2009). Modelling the atmospheric response over southern Africa to SST forcing in the southeast tropical Atlantic and southwest subtropical Indian Oceans. Int. J. Climatol., 29: 1001–1012.&lt;br /&gt;
&lt;br /&gt;
Hermes, J., and C. Reason (2009). Variability in sea-surface temperature and winds in the tropical south-east Atlantic Ocean and regional rainfall relationships. Int. J. Climatol., 29: 11–21.&lt;br /&gt;
&lt;br /&gt;
IPCC (2007). Summary for policymakers Climate Change 2007: Impacts, Adaptation and Vulnerability. Contribution of Working Group II to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change ed M L Parry, O F Canziani, J P Palutikof, P J van der Linden and C E Hanson (Cambridge: Cambridge University Press) pp 7-22.&lt;br /&gt;
&lt;br /&gt;
IPCC (2014). Climate Change 2014: Summary for Policymakers, Synthesis Report. Contribution of Working Groups I, II and III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change [Core Writing Team, R.K. Pachauri and L.A. Meyer (eds.)]. IPCC, Geneva, Switzerland, 151 pp.&lt;br /&gt;
&lt;br /&gt;
Li, J., Chen, Y.D., Gan, T.Y., Lau, N. (2018). Elevated increases in human-perceived temperature under climate warming. Nat. Clim. Chang. 8: 43–47. https://doi.org/10.1038/s41558-017-0036-2.&lt;br /&gt;
&lt;br /&gt;
Marchant, R., C. Mumbi, S. Behera, and T. Yamagata (2007). The Indian Ocean dipole—the unsung driver of climatic variability in East Africa. Afr. J. Ecol., 45: 4–16.&lt;br /&gt;
&lt;br /&gt;
Moss, R. H. et al. (2010). The next generation of scenarios for climate change research and assessment. Nature, Vol 463, 11 February 2010, doi:10.1038/nature08823.&lt;br /&gt;
&lt;br /&gt;
Pohl, B., N. Fauchereau, C. Reason, and M. Rouault (2010). Relationships between the Antarctic Oscillation, the Madden - Julian Oscillation, and ENSO, and Consequences for Rainfall Analysis. J. Clim., 23: 238–254.&lt;br /&gt;
&lt;br /&gt;
Rouault, M., P. Florenchie, N. Fauchereau, and C. Reason (2003). South East tropical Atlantic warm events and southern African rainfall. Geophys. Res. Lett., 30, doi:10.1029/2002GL014840.&lt;br /&gt;
&lt;br /&gt;
UNFCCC (2010). The Cancun Agreements. United Nations Framework Convention on Climate Change http://unfccc.int/meetings/cancunnov2010/meeting/6266.php, 2010.&lt;br /&gt;
&lt;br /&gt;
URT (2019). Water sector development programme. Environmental and social management framework (ESMF). Revised version. Ministry of Water.&lt;br /&gt;
&lt;br /&gt;
Vautard, R., Gobiet, A., Sobolowski, S., Kjellström, E., Stegehuis, A., Watkiss, P., Mendlik. T., Landgren, O., Nikulin, G., Teichmann, C. and Jacob, D. (2014). The European climate under a 2°C global warming. Environ. Res. Letters. Environ. Res. Lett. 9, 034006, doi:10.1088/1748-9326/9/3/034006.&lt;br /&gt;
&lt;br /&gt;
Vigaud, N., Y. Richard, M. Rouault, and N. Fauchereau (2009). Moisture transport between the South Atlantic Ocean and southern Africa: Relationships with summer rainfall and associated dynamics. Clim. Dyn., 32: 113–123.&lt;br /&gt;
&lt;br /&gt;
WHO (2017). Climate-resilient water safety plans: Managing health risks associated with climate variability and change. World Health Organization. ISBN: 978-92-4-151279-4. Retrieved from: https://www.who.int/water_sanitation_health/publications/climate-resilient-water-safety-plans/en/&lt;br /&gt;
&lt;br /&gt;
Previous Page: [[Chapter One: Introduction|Chapter One: Introduction]] &amp;lt;&amp;lt;  &amp;gt;&amp;gt; Next Page: [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]]&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=Chapter_Two:_Project_Planning&amp;diff=515</id>
		<title>Chapter Two: Project Planning</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=Chapter_Two:_Project_Planning&amp;diff=515"/>
		<updated>2020-03-31T10:52:19Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;&amp;lt;big&amp;gt;'''Chapter Two: Project Planning'''&amp;lt;/big&amp;gt;&lt;br /&gt;
Arguably, planning of water supply projects is considered to be one of the most important stages in the design. Thus, it is strongly advised and emphasized that much time should be spent to undertake proper project planning. A proper project planning will ensure effective and efficient completion of the project successfully. In this chapter, project planning is presented in seven parts that are detailed below. These include:&lt;br /&gt;
&lt;br /&gt;
* Planning considerations for water supply projects&lt;br /&gt;
* Project Planning steps&lt;br /&gt;
* Consulting the Integrated Water Resources Management and Development Plan&lt;br /&gt;
* Consult guideline for preparation of Water Safety Plan – resilient to climate change.&lt;br /&gt;
* Environmental and Social Impact Assessment (ESIA) and Strategic Environmental and Social Impact Assessment (SESIA) Compliance&lt;br /&gt;
* Potential Impacts of Climate Change on Water Supply Projects&lt;br /&gt;
* Participation of CBWSOs in Project Planning Stages&lt;br /&gt;
&lt;br /&gt;
=Chapter Two: Project Planning=&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
==2.1	Planning Considerations for Water Supply Projects ==&lt;br /&gt;
Before commencement of any development of a water project, it is essential to conduct project planning. Planning is a process that should entail the following:&lt;br /&gt;
•	Undertake ESIA and SESIA studies,&lt;br /&gt;
•	Engagement and involvement of the local community to instill the ownership, provide the local knowledge, project buy in and accommodate community needs and requirements,&lt;br /&gt;
•	Assess safe and reliable yield or discharge and quality of water source,&lt;br /&gt;
•	Determination of the system layout,&lt;br /&gt;
•	Conduct design of the water supply project,&lt;br /&gt;
•	Implement the project in terms of construction, operation and maintenance,&lt;br /&gt;
•	Work out to obtain a sound and robust project financing.&lt;br /&gt;
&lt;br /&gt;
It should be emphasized and stressed that collection of good quality, reliable, credible and enough data should be given high priority at all stages of project implementation. Population projection methods and their relevance for rural and urban settings or areas as recommended by the National Bureau of Statistics (NBS) have to be evaluated. Demographic features such as social and economic conditions have to be studied before design projections can be established. Also, water source reliability should be carried out before any further stage of project implementation.&lt;br /&gt;
==2.2	Project Planning Steps==&lt;br /&gt;
Project planning involves a series of steps that determine how project goals will be achieved. The goals may be solicited from the existing community or a strategic plan. In an event that there is not any plan, project plans can be developed through community meetings and gatherings, councils or board meetings, special focused group discussions or other planning processes. &lt;br /&gt;
&lt;br /&gt;
The main steps of project planning include:&lt;br /&gt;
* Step 1: Initiation&lt;br /&gt;
* Step 2: Pre-feasibility study&lt;br /&gt;
* Step 3: Feasibility study&lt;br /&gt;
* Step 4: Preliminary and Detailed Design&lt;br /&gt;
* Step 5: Project phasing&lt;br /&gt;
* Step 6: Procurement&lt;br /&gt;
* Step 7: Implementation/Construction&lt;br /&gt;
* Step 8: Operation and Maintenance (Management)&lt;br /&gt;
* Step 9: Performance Monitoring&lt;br /&gt;
&lt;br /&gt;
The planning of water supply projects can be represented diagrammatically by a step wise planning cycle as shown in Figure 2.1.&lt;br /&gt;
&lt;br /&gt;
==2.3	Pump Protection==&lt;br /&gt;
The following sections provide a brief description of each of the twelve project planning steps.&lt;br /&gt;
&lt;br /&gt;
===2.3.1	Initiation===&lt;br /&gt;
Initiation or sometimes referred to as triggering stage, is a step where initial ideas of the project are presented. Community mobilization through awareness raising is conducted at this stage. The whole idea is to inform the community on the start of the project, solicit community input and knowledge about the project area. Project common understanding is also expected to be realized at this step. &lt;br /&gt;
&lt;br /&gt;
The outcome of this stage of planning is to acquire an understanding of the community conditions and identify problems that prevent the community from achieving its long-range goals. Community conditions which must be collected includes aspects of the community such as: &lt;br /&gt;
* Its geographic location, &lt;br /&gt;
* Demographics, &lt;br /&gt;
* Ecosystem, &lt;br /&gt;
* History,e.t.c&lt;br /&gt;
&lt;br /&gt;
The data collection for the above information should employ community assessment methods.&lt;br /&gt;
&lt;br /&gt;
[[File:Volume I Figure 2.1 Projects Planning Process.png|thumb|Figure 2.1: Projects Planning Process]]&lt;br /&gt;
&lt;br /&gt;
(Source: Modified after Design Manual 3rd edition, 2009)&lt;br /&gt;
 &lt;br /&gt;
====2.3.1.1	Community Assessment Steps====&lt;br /&gt;
* Identify specific community problems that stand in the way of meeting community goals. Produce a community problem statement,&lt;br /&gt;
* Creates a work plan for addressing problems and attaining the goals, &lt;br /&gt;
* Describe measurable beneficial impacts to the community that result from the project’s implementation, &lt;br /&gt;
* Determine the level of resources or funding necessary to implement the project.&lt;br /&gt;
* Solicit community social economic assessment report from Local Government Authorities for use in choice of technology to achieve project sustainability&lt;br /&gt;
&lt;br /&gt;
====2.3.1.2	 Methods of conducting community assessment====&lt;br /&gt;
Two methods can be employed for conducting community assessment. They are comprehensive and strategic planning.&lt;br /&gt;
&lt;br /&gt;
=====2.3.1.2.1	Comprehensive community assessment=====&lt;br /&gt;
This process should involve:&lt;br /&gt;
* Completing a community-wide needs assessment to engage the community in identifying and prioritizing all long-range goals and the community problems preventing the achievement of those goals, &lt;br /&gt;
* Next, the community is involved in the process of developing a method to accomplish long-range goals,  &lt;br /&gt;
* Discussing initial ways to overcome the problems &lt;br /&gt;
* Develop measures to monitor progress towards achieving those goals. &lt;br /&gt;
&lt;br /&gt;
Comprehensive plans require at least a year to complete and should cover a five- to ten-year time span. &lt;br /&gt;
&lt;br /&gt;
======2.3.1.2.2	Strategic community assessment======&lt;br /&gt;
This is a process used when a community or an organization already has a comprehensive plan and wants to move forward to achieve its long-range goals. Strategic planning involves:&lt;br /&gt;
Participation of the community in identifying problems that stand between the community and its goals and to move the community towards realizing its long-range vision. &lt;br /&gt;
&lt;br /&gt;
The product of strategic planning, simply called the “strategic plan,” builds on pre-established long-range goals by designing projects related to one or more of these goals. A strategic plan generally takes at least six months to complete.&lt;br /&gt;
&lt;br /&gt;
===2.3.2	Pre-feasibility Study===&lt;br /&gt;
The pre-feasibility study stage involves initial fieldwork and studies of alternative water resource development plans. The report issued is an outline of possibilities and a list of all the fieldwork activities that need to be accomplished at a feasibility study or even a preliminary engineering design stage.&lt;br /&gt;
&lt;br /&gt;
The objective of this initial study is to determine whether it is worthwhile to proceed with more detailed investigations. In other words at this stage, various projects or alternatives are screened and this should normally reduce the number of options considered feasible to no more than three or so. The report should, however, contain recommendations on the proposed project and how to proceed with the detailed investigations.&lt;br /&gt;
&lt;br /&gt;
These should include indications on the following:&lt;br /&gt;
&lt;br /&gt;
* Data to be collected,&lt;br /&gt;
* Remaining alternatives to be considered and investigated,&lt;br /&gt;
* Professional human resources required,&lt;br /&gt;
* Estimate of time that will be taken or needed,&lt;br /&gt;
* Budgetary financial requirements.&lt;br /&gt;
&lt;br /&gt;
The above are considered taking into account:&lt;br /&gt;
&lt;br /&gt;
* Long term needs,&lt;br /&gt;
* Deficiencies in the existing system (if any),&lt;br /&gt;
* Phases of project implementation.&lt;br /&gt;
&lt;br /&gt;
Briefly, the pre-feasibility report should give an outline of the future development, which seems most appropriate to provide the project area with water in the long term. The other major aim may be to select a short-term project that may be implemented to overcome any immediate needs (crash programme) while the long-term project is being prepared. &lt;br /&gt;
&lt;br /&gt;
===2.3.3	Feasibility Study===&lt;br /&gt;
The feasibility study stage develops the pre-feasibility work further and ends with a Report which normally concentrates on the project alternatives that were recommended for more detailed consideration at the pre-feasibility stage.&lt;br /&gt;
&lt;br /&gt;
The study has to be carried out by a team of competent and experienced personnel from the Ministry, RUWASA and WWSA or with the help of a private sector. At this stage, the following should be achieved:&lt;br /&gt;
&lt;br /&gt;
* Collection of sufficient design data,&lt;br /&gt;
* Appraise the alternatives,&lt;br /&gt;
* Alternative plans (projects) adequately studied and evaluated,&lt;br /&gt;
* Socio-economic analysis adequately conducted and completed&lt;br /&gt;
* Solicit the views and preferences with community in an open meeting&lt;br /&gt;
* Discuss the merits and demerits with community representatives&lt;br /&gt;
* Rank alternatives on the basis of appropriate costing method and perceived ability of community to afford the costs of operation and maintenance and reach agreement in principle with concerned water officials.&lt;br /&gt;
* Inform the community reasons for selection of the alternative(s) and seek their agreement and approval.&lt;br /&gt;
* Conduct Environmental Impact assessment (EIA). For larger projects a statement on Life Cycle Assessment should be included indicating the extent of quantitative and other relevant information currently available,&lt;br /&gt;
* Preliminary engineering design done, including a review of alternative materials,&lt;br /&gt;
* Preliminary cost estimates done,&lt;br /&gt;
* Economic internal rate of return and financial internal rate of return,&lt;br /&gt;
* Carry out design to a level sufficient to enable construction to proceed either using local (District) based contractors or a Force Account approach using local sub-contractors as considered feasible and appropriate,&lt;br /&gt;
* Most feasible project (least cost) selected, &lt;br /&gt;
* Feasibility report prepared and presented to the authorities for approval&lt;br /&gt;
&lt;br /&gt;
The report may also include interim progress reports, appendices of data collected during the detailed study. The feasibility report should be presented as a supporting document to apply for financing from the financing agencies.&lt;br /&gt;
====2.3.3.1	 Water Supply Projects Ranking and Technology Selection Criteria====&lt;br /&gt;
=====2.3.3.1.1	Ranking of Projects=====&lt;br /&gt;
Projects to be implemented should be ranked on the basis of the following criteria;&lt;br /&gt;
* Type of technology,&lt;br /&gt;
* Quantity of water,&lt;br /&gt;
* ESIA Report comments,&lt;br /&gt;
* Negative environment impact,&lt;br /&gt;
* Quality of water available,&lt;br /&gt;
* Cost/benefit analysis, &lt;br /&gt;
* Walking distance scheme complexity.&lt;br /&gt;
&lt;br /&gt;
=====2.3.3.1.2	Choice of Technology=====&lt;br /&gt;
As far as possible ranking of project selection is concerned, technology choice should be based on progressive consideration of:&lt;br /&gt;
* Hand pump(s) from proven permanent deep hand dug well(s) or shallow borehole(s),&lt;br /&gt;
* Gravity scheme from protected spring,&lt;br /&gt;
* Medium or deep well with appropriate hand pump (rotary type),&lt;br /&gt;
* Pumped / Piped Scheme Electrical Driven,&lt;br /&gt;
* Pumped/Piped Scheme Solar Driven.&lt;br /&gt;
&lt;br /&gt;
For point water sources or simple distribution systems, a prime location for a domestic point should be the village primary school followed by a village health facility (if any). Provision of improved sanitation and hand washing facilities at both primary school and health facility should also receive priority consideration in any village scheme. Use the relevant WASH guidelines for design of the washing facilities.&lt;br /&gt;
&lt;br /&gt;
===2.3.4	Preliminary and Detailed Design===&lt;br /&gt;
After the feasibility report is presented and approved, the preliminary and the preferred alternative should be selected and the finances sought. The following should be considered while conducting the design:&lt;br /&gt;
* The Engineer should prepare the preliminary engineering design and then the detailed or final project report,  &lt;br /&gt;
* These reports should provide the basis for implementation,  &lt;br /&gt;
* The initial report has to provide the design basics which are then developed further in the detailed design of the project including working drawings and tender documents,  &lt;br /&gt;
* They should however include a review of all relevant aspects of this DCOM Manual and either accept or otherwise indicate, complete with detailed reasoning, why different criteria is proposed. &lt;br /&gt;
&lt;br /&gt;
In addition, the report should address the following:&lt;br /&gt;
* The issue of costing being adopted and requirement for extent of whole life cycle analysis and adaptation of costing,  &lt;br /&gt;
* Consideration of the environmental impacts of the project and its envisaged elements,  &lt;br /&gt;
* Issue of climate change and its possible effects on the project being designed. &lt;br /&gt;
&lt;br /&gt;
It should be noted that the conceptual designs provided at the feasibility study or preliminary engineering stages are generally inadequate for the construction of the project. Foremost, the Engineer arranges for any outstanding detailed field investigations, surveys and data collection. Based on the detailed field data collected; detailed designs, plans and estimates are prepared.&lt;br /&gt;
&lt;br /&gt;
Detailed designs should include:&lt;br /&gt;
* Statistical analysis of data collected for the population and demand projections; hydrological ,hydrogeological  and meteorological data,&lt;br /&gt;
* Least cost lay-outs for different components of the project, i.e. treatment plants, hydraulic and structural works,&lt;br /&gt;
* Structural and stability computations of different structures,&lt;br /&gt;
* Calculations for pumps, motors, power generators and other machinery and equipment,&lt;br /&gt;
* Engineering analysis for deciding the most economic size of delivery mains.&lt;br /&gt;
* Hydraulic computations for the distribution system,&lt;br /&gt;
* Bills of quantities.&lt;br /&gt;
* Detailed design should include the following:&lt;br /&gt;
&lt;br /&gt;
====2.3.4.1	Detailed Engineering Drawings====&lt;br /&gt;
These should include:&lt;br /&gt;
&lt;br /&gt;
* Index plan showing overall layout of the project,&lt;br /&gt;
* Schematic diagram showing levels of salient components of the project (may not necessarily be to scale),&lt;br /&gt;
* Detailed plans and sections in scale for the headwords, treatment plants, clear water storage tank, pumping station, in a scale 1:20 to 1:100 depending on the details and size of the works,&lt;br /&gt;
* Detailed structural plans for structures, intake, treatment plant, clear water reservoir etc., in a scale of 1:20,&lt;br /&gt;
* Index plan of the distribution system normally in an appropriate scale,&lt;br /&gt;
* Longitudinal sections of the delivery main and details of appurtenances in scales: Horizontal scale 1:500 to 1:5000 depending on distance and details Vertical scale 1:20 to 1:100 depending on the terrain surface undulations.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.2		Detailed estimates of capital costs====&lt;br /&gt;
Project cost estimates should be based on unit costs derived from recent projects of a similar magnitude, complexity and remoteness from or proximity to ports or major urban areas.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.3	 Detailed estimates of recurrent costs====&lt;br /&gt;
As far as possible this should be based on unit costs provided by the operating authority or from schemes of a similar size and nature.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.4	 Anticipated revenue====&lt;br /&gt;
These should be based on the recommendations made regarding tariff structures or provided by the operating authority or regulator.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.5	 Detailed design report====&lt;br /&gt;
A report should accompany the detailed designs, plans and estimates elaborating on the:&lt;br /&gt;
* Engineering aspects,&lt;br /&gt;
* Financial aspects,&lt;br /&gt;
* Administrative aspects, &lt;br /&gt;
* Tender documents &lt;br /&gt;
* Specifications.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.6	 Project write-up to be submitted to potential financiers====&lt;br /&gt;
Each Development Partner may have a different pattern of project presentation for financial request. The project document should therefore follow more guidelines as indicated by the financiers or the local funding sources where applicable.&lt;br /&gt;
&lt;br /&gt;
====2.3.5	Project Phasing====&lt;br /&gt;
Sometimes the implementation of a project is carried out in phases due to among other things, the following reasons:&lt;br /&gt;
* Financial resources available,&lt;br /&gt;
* Opportunity cost of money,&lt;br /&gt;
* Economies of scale,&lt;br /&gt;
* Growth rate in the area,&lt;br /&gt;
* Rate of development in the area,&lt;br /&gt;
* The design (working) life of various installations,&lt;br /&gt;
* Development in levels of service,&lt;br /&gt;
* New technology or method that needs piloting before rolling it out&lt;br /&gt;
Once the basic design period is decided (usually between 10 and 20 years) and water demand is computed for different years, the different elements can be phased. Exceptions do occur where financial assistance capital is being used and there is fear or a probability that further trunches will not be available just a few years later.&lt;br /&gt;
&lt;br /&gt;
Generally, phasing should be undertaken as follows: &lt;br /&gt;
(i)	Dams, river and spring intakes, should be implemented in a single phase to cover all of the ultimate design demand or the hydrologically calculated water availability. This is particularly significant for dams as flood spillways form an expensive integral part and the need to raise a spillway inlet and deal with the additional energy at its exit is usually very costly.&lt;br /&gt;
(ii)	Boreholes to be constructed in Multiple Phases according to the growth in demand.&lt;br /&gt;
(iii)	Treatment plants and storage tanks to be constructed stepwise or in phases, according to the projected growth in demand.&lt;br /&gt;
(iv)	Mechanical installations to be implemented in Multiple Phases according to the design life of the equipment.&lt;br /&gt;
(v)	Pump houses constructed in a Single Phase with space for additional mechanical plant.&lt;br /&gt;
(vi)	Rising mains and main conduits between units to be constructed to cover the ultimate demand in a single Phase.&lt;br /&gt;
(vii)	Long transmission mains to be constructed as two parallel lines in a single Phase where funds allow or in Two Phases where not. It can be advantageous to dedicate one of two parallel transmission mains to supplying water to the terminal reservoir whilst using the second for a mix of local distribution (daytime) and conveyance to the terminal reservoir (night time).&lt;br /&gt;
(viii)	Distribution systems to be constructed according to the growth in development in Multiple Phases.&lt;br /&gt;
&lt;br /&gt;
===2.3.6	Procurement===&lt;br /&gt;
====2.3.6.1	Preparation of Tender Documents====&lt;br /&gt;
The Procurement Management Unit (PMU) using the approved templates as guided by PPRA documentation undertakes preparation of tender documents. In preparing the tender documents undertaken by PMU, unit rate contract is normally adopted for project components such as intake, delivery mains, distribution system, storage tanks and other appurtenances. For specialized areas like the treatment plants and pumping stations it may be necessary to prepare separate tenders for the supply and installation of such facilities. The superstructure may still be included in the main contract bill of quantities. As much as possible one contract is preferred. The suppliers of such specialized equipment would then be included as sub-contractors of the main contractor. Important documents included in contract documents includes:&lt;br /&gt;
* Letter of Invitation to Tender &lt;br /&gt;
* Instruction to Tenderers &lt;br /&gt;
* General Conditions of Contract&lt;br /&gt;
* Special Conditions of Contract&lt;br /&gt;
* Drawings &lt;br /&gt;
* Specifications &lt;br /&gt;
* Bills of Quantities&lt;br /&gt;
* Tender Forms&lt;br /&gt;
* Security Forms &lt;br /&gt;
* Anti-bribery Pledge&lt;br /&gt;
* Schedule of Additional Information&lt;br /&gt;
* Information Data&lt;br /&gt;
&lt;br /&gt;
====2.3.6.2	Tendering process====&lt;br /&gt;
This process involves use of public procurement act to select service providers as detailed in following steps; &lt;br /&gt;
* Issue of tender documents&lt;br /&gt;
* Submission and receipt of tenders&lt;br /&gt;
* Opening of tenders&lt;br /&gt;
* Evaluation of tenders&lt;br /&gt;
* Award of tender&lt;br /&gt;
* Signing of contract agreement&lt;br /&gt;
&lt;br /&gt;
===2.3.7	Implementation/Construction Stage===&lt;br /&gt;
Construction stage includes contract management, Contract supervision and administration.&lt;br /&gt;
====2.3.7.1	Contract Management====&lt;br /&gt;
Contract management entails the following;&lt;br /&gt;
* Contract Management Plan (CMP),&lt;br /&gt;
* Contract Delivery Follow-up,&lt;br /&gt;
* Work progress monitoring &amp;amp; control,  &lt;br /&gt;
* All projects executed must have a completion report (as constructed built reports and drawings). It is essential that Engineers or Foremen keep an up to date record of all project activities including all changes to the original design with reasons for this clearly indicated as well as the approving authority.&lt;br /&gt;
* Initial and Final Acceptance of the Works&lt;br /&gt;
* Contract Close Out&lt;br /&gt;
====2.3.7.2	Contract supervision and administration ====&lt;br /&gt;
During construction stage, it is necessary to consider the following;&lt;br /&gt;
* Each phase of the project implementation should be planned in detail using techniques such as the Critical Path Method (CPM) or Programme Evaluation or/and Review Technique (PERT ) to ensure time control,&lt;br /&gt;
* Work together with the Contractor to prepare a Quality Assurance Plan which shall narrate the scope of the works and the expected quality requirements for the project, the role of the participants in ensuring quality requirements are met&lt;br /&gt;
* Obtain a cash flow forecast from the contractor, and make the Client aware of his payment obligations based on the forecast&lt;br /&gt;
* Keep a close track of all contractors approved claims and adjust the contract price to reflect increase or decrease in the contract price&lt;br /&gt;
* Detailed information in procurement, contract management, contract supervision and administration is detailed well in chapter three and four of Volume III Construction Supervision for Water Supply and Sanitation Projects.&lt;br /&gt;
&lt;br /&gt;
===2.3.8	Operation and Maintenance Stage===&lt;br /&gt;
   This process takes over after the project completion, it involves;&lt;br /&gt;
* Preparation of O&amp;amp;M Plan,&lt;br /&gt;
* Development of Individual Unit Plans for O&amp;amp;M,&lt;br /&gt;
* Plan for capacity Building of O&amp;amp;M Personnel,&lt;br /&gt;
* Plan for Providing Spares and Tools,&lt;br /&gt;
* Plan for Water Audit and Leakage Control,&lt;br /&gt;
* Plan for Efficient Use of Power,&lt;br /&gt;
* Plan for sound financial management system,&lt;br /&gt;
* Plan for Information Education Communication for Water and Sanitation Services,&lt;br /&gt;
* Reports and Record Keeping,&lt;br /&gt;
* Develop appropriate maintenance schedule and check lists,&lt;br /&gt;
* Utilize Standard Operating Procedures,&lt;br /&gt;
* Utilize Water Safety Plans.&lt;br /&gt;
&lt;br /&gt;
Detailed information on planning for operation and maintenance is found in chapter three and four of Volume IV Operation and Maintenance of Water Supply and Sanitation Projects&lt;br /&gt;
&lt;br /&gt;
===2.3.9	Performance Monitoring===&lt;br /&gt;
The aim of the project is to provide the services uninterrupted. To ensure this, a proper monitoring mechanism of the performance of the project should be prepared. Such a mechanism could include proper procedures for procurement and distribution of spare parts, fuel, replacement, a maintenance programme for the project including personnel at the village, District and if necessary at Regional and National levels also. Likewise a water quality surveillance procedure should be instituted in the framework of the existing mechanism.&lt;br /&gt;
&lt;br /&gt;
==2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans==&lt;br /&gt;
It is imperative that during planning of the water supply and sanitation project, designer should consult the Integrated Water Resources Management and Development (IWRMD) plan for a basin where the project is planned to be executed. The development of an IWRMD Plan is a key objective of the water resources component of the Water Sector Development Programme 2006-2025. It is a legal requirement provided for in the Water Resources Management Act, No. 11 of 2009. The plan provides a blueprint for sustainable development and management of the basin’s water resources. &lt;br /&gt;
&lt;br /&gt;
Thus, a water supply and sanitation project designer is advised and encouraged to consult IWRMD plans as they provide:&lt;br /&gt;
&lt;br /&gt;
* The status of water resource availability (both quantity and quality) in the basin,&lt;br /&gt;
* Water data and information necessary for the design of the projects,&lt;br /&gt;
* Framework for water allocations among its competing demands,&lt;br /&gt;
* Water demand for water related sectors,&lt;br /&gt;
* Stakeholders consultation plan.&lt;br /&gt;
&lt;br /&gt;
===2.4.1	Status of Development and Implementation of IWRMD Plans===&lt;br /&gt;
By the time of development of this DCOM manual, IWRMD plans had been developed for six (6) out of the nine basins. The six basins are:&lt;br /&gt;
* Rufiji River Basin,&lt;br /&gt;
* Ruvuma and Southern Coast Basin,&lt;br /&gt;
* Lake Tanganyika Basin,&lt;br /&gt;
* Lake Nyasa Basin,&lt;br /&gt;
* Internal Drainage and&lt;br /&gt;
* Lake Rukwa Basin&lt;br /&gt;
&lt;br /&gt;
It was reported that the development of IWRMD plans for Lake Victoria Basin and Wami/Ruvu basins were on-going. &lt;br /&gt;
&lt;br /&gt;
IWRMD plans implementation challenges have been observed in some basins. These include:&lt;br /&gt;
&lt;br /&gt;
* Inadequate funding to implement plans recommendations,&lt;br /&gt;
* Some plans are not implementable because of including unrealistic recommendations,&lt;br /&gt;
* Some plans are considered to have been more of studies rather than plans,&lt;br /&gt;
* Inadequate human resources capacity to implement them,&lt;br /&gt;
* As required by EMA, ESIAs have not been conducted, contrary to the requirement&lt;br /&gt;
&lt;br /&gt;
===2.4.2	Components of IWRMD Plans===&lt;br /&gt;
The developed IWRMD plans are expected to have the following main components:&lt;br /&gt;
* Component 1: Inventory and review of water availability, use and demand,&lt;br /&gt;
* Component 2: Institutional, Policy and legal framework,&lt;br /&gt;
* Component 3: Sector/Thematic Water Plans,&lt;br /&gt;
* Component 4: Integrated Water Resources Management and Development Plan, &lt;br /&gt;
* Component 5: IWRMD Plan Implementation Strategy and Action Plan.&lt;br /&gt;
&lt;br /&gt;
The production capacity of a source is very important in planning a water supply system. An estimate of the water that can be reliably produced by a water source like a well or spring gives the planner a basis to decide for or against its development. For the source(s) to be considered adequate, they must at least satisfy the maximum daily demand of the area to be served.&lt;br /&gt;
&lt;br /&gt;
==2.5		Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change ==&lt;br /&gt;
&lt;br /&gt;
Water Safety Plan (WSP) is the most effective means of consistently ensuring the safety of a drinking-water supply through the use of a comprehensive risk assessment and risk management approach that encompasses all steps in water supply from the catchment to the consumer (WHO, 2017). The approach enables the operators and managers of water utilities to know the system thoroughly, identify where and how problems could arise, put multiple barriers and management systems in place to stop the problems before they happen and making all parts of the system work properly so as to ensure the safety and acceptability of a drinking water supply intended for human consumption and other domestic uses as summarized in the WHO safe water chain frameworks.&lt;br /&gt;
&lt;br /&gt;
Thus, during the planning phase, a designer should consult guidelines for the preparation of Water Safety Plans - Resilient to Climate Change, which has been prepared and published by Ministry of Water (MoW, 2015)&lt;br /&gt;
&lt;br /&gt;
==2.6	Environmental and Social Impact Assessment Compliance==&lt;br /&gt;
Section 81 of the Environmental Management Act (Cap 191) requires all developers of projects identified in the 3rd Schedule of the Act and detailed in the 1st Schedule of the Environmental Management (Environmental Impact Assessment And Audit) (Amendment) Regulations, 2018, to undertake Environmental Impact Assessment (EIA). Section 82 of EMA (Cap 181) requires that the EIA be carried out prior to the commencement or financing of the project. Procedures for carrying out the EIA, identified under the EIA and Audit  (Amendment) Regulations of 2018 identify eight steps to be followed. According to EIA and Audit (Amendment) Regulations of 2018, projects are classified into the following categories, namely:&lt;br /&gt;
&lt;br /&gt;
(a) “A” category for Mandatory projects;&lt;br /&gt;
 (b) “B1” category for Borderline Project;&lt;br /&gt;
(c) “B2” category for Non-Mandatory; and&lt;br /&gt;
(d) “Special Category&lt;br /&gt;
&lt;br /&gt;
So it is imperative that a proponent and developer of any water supply and sanitation project categorizes their project prior to actual project implementation for the same.&lt;br /&gt;
&lt;br /&gt;
===2.6.1	Procedures for Conducting ESIA in Tanzania===&lt;br /&gt;
Procedures for carrying out the ESIA, identified under the EIA and Audit (Amendment) Regulations of 2018 identify eight key steps to be followed in the EIA process in Tanzania. These are:&lt;br /&gt;
&lt;br /&gt;
* Step 1: Registration,&lt;br /&gt;
* Step 2: Screening, &lt;br /&gt;
* Step 3: Scoping,&lt;br /&gt;
* Step 4: Environmental Assessment,&lt;br /&gt;
* Step 5: Review,&lt;br /&gt;
* Step 6: Recommendations of the Technical Advisory Committee (TAC),&lt;br /&gt;
* Step 7: Submission To The Minister For Environment,&lt;br /&gt;
* Step 8: Approval of the EIS.&lt;br /&gt;
&lt;br /&gt;
It is recommended to consult NEMC guidelines and Environmental Management (Environmental Impact Assessment And Audit) (Amendment) Regulations, 2018 for more details. Also, the following Ministry of Water guidelines, accessible at have to be consulted.&lt;br /&gt;
a)	Guidelines of Good Environmental and Social Practices (GGESP) of July 2019,&lt;br /&gt;
b)	Environmental and Social Management Framework (ESMF) of July 2019.&lt;br /&gt;
&lt;br /&gt;
===2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance===&lt;br /&gt;
&lt;br /&gt;
Section 105 part (2) of the Environmental Act requires that wherever there is a major water project planned for construction, the Ministry responsible for water should conduct Strategic Environmental and Social Assessment. The strategic environmental assessment shall asses the area marked for development and include:&lt;br /&gt;
&lt;br /&gt;
* Baseline environmental conditions and status of natural resources,&lt;br /&gt;
* Identification of ecological sensitive and protected areas,&lt;br /&gt;
* Identification and description of communities around the area,&lt;br /&gt;
* Existing social-economic conditions,&lt;br /&gt;
* Existing economic activities and infrastructure.&lt;br /&gt;
The strategic environmental and social assessment shall be submitted to the Minister responsible for Environment for approval before the planning process.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
==2.7	Potential Impacts of Climate Change on Water Supply Projects==&lt;br /&gt;
It should be emphasized that immediately the project is conceived, hydrological, rainfall and other meteorological data collection must be initiated. In addition and given the long design life of such structures, consideration must be given to the possible impacts of climate change. Detailed account of predictions and impacts of climate change on water supply projects is provided in Appendix A.&lt;br /&gt;
&lt;br /&gt;
URT (2019) has recommended strategies and plans to adapt risks from climate change. The design related strategies of infrastructure, which a designer should consider while planning for water supply projects include:&lt;br /&gt;
&lt;br /&gt;
* Where possible, have at least two sources of supply at different locations. Build superstructures above high flood-line level.&lt;br /&gt;
* Adopt energy-efficiency programmes and, where possible, select facilities which require less power consumption.&lt;br /&gt;
* Monitor wells near coastlines to prevent salinization. If climate change causes sea levels to rise dramatically, even aquifers that have been sustainably utilized can suffer salinization.&lt;br /&gt;
* Utilize renewable energy sources.&lt;br /&gt;
&lt;br /&gt;
Guidelines for resiliency to climate change for urban water supply utilities have been published by the Ministry of Water. &lt;br /&gt;
&lt;br /&gt;
==2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages==&lt;br /&gt;
As explained in detail in section 2.1 of this volume, the CBWSOs have to  be involved in the complete life cycle of the project including ensuring their sustainability during operation and maintenance of the projects under the overall coordination of WSSAs and RUWASA.&lt;br /&gt;
&lt;br /&gt;
==2.9	References==&lt;br /&gt;
Asadieh, B. and Krakauer, N.Y. (2016). Impacts of changes in precipitation amount and distribution on water resources studied using a model rainwater harvesting system. J. Am. Water Resour. Assoc. 52: 1450–1471.https://doi.org/10.1111/ 1752-1688.12472.&lt;br /&gt;
&lt;br /&gt;
Gebrechorkos, S. H., Hülsmann, S., &amp;amp; Bernhofer, C. (2019). Regional climate projections for impact assessment studies in East Africa. Environmental Research Letters, 14(4), 044031. https://doi.org/10.1088/1748-9326/ab055a&lt;br /&gt;
&lt;br /&gt;
Giannini, A., M. Biasutti, I. Held, and A. Sobel (2008). A global perspective on African climate. Clim. Change, 90: 359–383.&lt;br /&gt;
&lt;br /&gt;
Hansingo, K., and C. Reason (2008). Modelling the atmospheric response to SST dipole patterns in the South Indian Ocean with a regional climate model. Meteorol. Atmos. Phys., 100: 37–52.&lt;br /&gt;
&lt;br /&gt;
Hansingo, K., and C. Reason (2009). Modelling the atmospheric response over southern Africa to SST forcing in the southeast tropical Atlantic and southwest subtropical Indian Oceans. Int. J. Climatol., 29: 1001–1012.&lt;br /&gt;
&lt;br /&gt;
Hermes, J., and C. Reason (2009). Variability in sea-surface temperature and winds in the tropical south-east Atlantic Ocean and regional rainfall relationships. Int. J. Climatol., 29: 11–21.&lt;br /&gt;
&lt;br /&gt;
IPCC (2007). Summary for policymakers Climate Change 2007: Impacts, Adaptation and Vulnerability. Contribution of Working Group II to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change ed M L Parry, O F Canziani, J P Palutikof, P J van der Linden and C E Hanson (Cambridge: Cambridge University Press) pp 7-22.&lt;br /&gt;
&lt;br /&gt;
IPCC (2014). Climate Change 2014: Summary for Policymakers, Synthesis Report. Contribution of Working Groups I, II and III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change [Core Writing Team, R.K. Pachauri and L.A. Meyer (eds.)]. IPCC, Geneva, Switzerland, 151 pp.&lt;br /&gt;
&lt;br /&gt;
Li, J., Chen, Y.D., Gan, T.Y., Lau, N. (2018). Elevated increases in human-perceived temperature under climate warming. Nat. Clim. Chang. 8: 43–47. https://doi.org/10.1038/s41558-017-0036-2.&lt;br /&gt;
&lt;br /&gt;
Marchant, R., C. Mumbi, S. Behera, and T. Yamagata (2007). The Indian Ocean dipole—the unsung driver of climatic variability in East Africa. Afr. J. Ecol., 45: 4–16.&lt;br /&gt;
&lt;br /&gt;
Moss, R. H. et al. (2010). The next generation of scenarios for climate change research and assessment. Nature, Vol 463, 11 February 2010, doi:10.1038/nature08823.&lt;br /&gt;
&lt;br /&gt;
Pohl, B., N. Fauchereau, C. Reason, and M. Rouault (2010). Relationships between the Antarctic Oscillation, the Madden - Julian Oscillation, and ENSO, and Consequences for Rainfall Analysis. J. Clim., 23: 238–254.&lt;br /&gt;
&lt;br /&gt;
Rouault, M., P. Florenchie, N. Fauchereau, and C. Reason (2003). South East tropical Atlantic warm events and southern African rainfall. Geophys. Res. Lett., 30, doi:10.1029/2002GL014840.&lt;br /&gt;
&lt;br /&gt;
UNFCCC (2010). The Cancun Agreements. United Nations Framework Convention on Climate Change http://unfccc.int/meetings/cancunnov2010/meeting/6266.php, 2010.&lt;br /&gt;
&lt;br /&gt;
URT (2019). Water sector development programme. Environmental and social management framework (ESMF). Revised version. Ministry of Water.&lt;br /&gt;
&lt;br /&gt;
Vautard, R., Gobiet, A., Sobolowski, S., Kjellström, E., Stegehuis, A., Watkiss, P., Mendlik. T., Landgren, O., Nikulin, G., Teichmann, C. and Jacob, D. (2014). The European climate under a 2°C global warming. Environ. Res. Letters. Environ. Res. Lett. 9, 034006, doi:10.1088/1748-9326/9/3/034006.&lt;br /&gt;
&lt;br /&gt;
Vigaud, N., Y. Richard, M. Rouault, and N. Fauchereau (2009). Moisture transport between the South Atlantic Ocean and southern Africa: Relationships with summer rainfall and associated dynamics. Clim. Dyn., 32: 113–123.&lt;br /&gt;
&lt;br /&gt;
WHO (2017). Climate-resilient water safety plans: Managing health risks associated with climate variability and change. World Health Organization. ISBN: 978-92-4-151279-4. Retrieved from: https://www.who.int/water_sanitation_health/publications/climate-resilient-water-safety-plans/en/&lt;br /&gt;
&lt;br /&gt;
Previous Page: [[Chapter One: Introduction|Chapter One: Introduction]] &amp;lt;&amp;lt;  &amp;gt;&amp;gt; Next Page: [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]]&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=Chapter_Two:_Project_Planning&amp;diff=514</id>
		<title>Chapter Two: Project Planning</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=Chapter_Two:_Project_Planning&amp;diff=514"/>
		<updated>2020-03-31T10:51:00Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;Arguably, planning of water supply projects is considered to be one of the most important stages in the design. Thus, it is strongly advised and emphasized that much time should be spent to undertake proper project planning. A proper project planning will ensure effective and efficient completion of the project successfully. In this chapter, project planning is presented in seven parts that are detailed below. These include:&lt;br /&gt;
&lt;br /&gt;
* Planning considerations for water supply projects&lt;br /&gt;
* Project Planning steps&lt;br /&gt;
* Consulting the Integrated Water Resources Management and Development Plan&lt;br /&gt;
* Consult guideline for preparation of Water Safety Plan – resilient to climate change.&lt;br /&gt;
* Environmental and Social Impact Assessment (ESIA) and Strategic Environmental and Social Impact Assessment (SESIA) Compliance&lt;br /&gt;
* Potential Impacts of Climate Change on Water Supply Projects&lt;br /&gt;
* Participation of CBWSOs in Project Planning Stages&lt;br /&gt;
&lt;br /&gt;
=Chapter Two: Project Planning=&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
==2.1	Planning Considerations for Water Supply Projects ==&lt;br /&gt;
Before commencement of any development of a water project, it is essential to conduct project planning. Planning is a process that should entail the following:&lt;br /&gt;
•	Undertake ESIA and SESIA studies,&lt;br /&gt;
•	Engagement and involvement of the local community to instill the ownership, provide the local knowledge, project buy in and accommodate community needs and requirements,&lt;br /&gt;
•	Assess safe and reliable yield or discharge and quality of water source,&lt;br /&gt;
•	Determination of the system layout,&lt;br /&gt;
•	Conduct design of the water supply project,&lt;br /&gt;
•	Implement the project in terms of construction, operation and maintenance,&lt;br /&gt;
•	Work out to obtain a sound and robust project financing.&lt;br /&gt;
&lt;br /&gt;
It should be emphasized and stressed that collection of good quality, reliable, credible and enough data should be given high priority at all stages of project implementation. Population projection methods and their relevance for rural and urban settings or areas as recommended by the National Bureau of Statistics (NBS) have to be evaluated. Demographic features such as social and economic conditions have to be studied before design projections can be established. Also, water source reliability should be carried out before any further stage of project implementation.&lt;br /&gt;
==2.2	Project Planning Steps==&lt;br /&gt;
Project planning involves a series of steps that determine how project goals will be achieved. The goals may be solicited from the existing community or a strategic plan. In an event that there is not any plan, project plans can be developed through community meetings and gatherings, councils or board meetings, special focused group discussions or other planning processes. &lt;br /&gt;
&lt;br /&gt;
The main steps of project planning include:&lt;br /&gt;
* Step 1: Initiation&lt;br /&gt;
* Step 2: Pre-feasibility study&lt;br /&gt;
* Step 3: Feasibility study&lt;br /&gt;
* Step 4: Preliminary and Detailed Design&lt;br /&gt;
* Step 5: Project phasing&lt;br /&gt;
* Step 6: Procurement&lt;br /&gt;
* Step 7: Implementation/Construction&lt;br /&gt;
* Step 8: Operation and Maintenance (Management)&lt;br /&gt;
* Step 9: Performance Monitoring&lt;br /&gt;
&lt;br /&gt;
The planning of water supply projects can be represented diagrammatically by a step wise planning cycle as shown in Figure 2.1.&lt;br /&gt;
&lt;br /&gt;
==2.3	Pump Protection==&lt;br /&gt;
The following sections provide a brief description of each of the twelve project planning steps.&lt;br /&gt;
&lt;br /&gt;
===2.3.1	Initiation===&lt;br /&gt;
Initiation or sometimes referred to as triggering stage, is a step where initial ideas of the project are presented. Community mobilization through awareness raising is conducted at this stage. The whole idea is to inform the community on the start of the project, solicit community input and knowledge about the project area. Project common understanding is also expected to be realized at this step. &lt;br /&gt;
&lt;br /&gt;
The outcome of this stage of planning is to acquire an understanding of the community conditions and identify problems that prevent the community from achieving its long-range goals. Community conditions which must be collected includes aspects of the community such as: &lt;br /&gt;
* Its geographic location, &lt;br /&gt;
* Demographics, &lt;br /&gt;
* Ecosystem, &lt;br /&gt;
* History,e.t.c&lt;br /&gt;
&lt;br /&gt;
The data collection for the above information should employ community assessment methods.&lt;br /&gt;
&lt;br /&gt;
[[File:Volume I Figure 2.1 Projects Planning Process.png|thumb|Figure 2.1: Projects Planning Process]]&lt;br /&gt;
&lt;br /&gt;
(Source: Modified after Design Manual 3rd edition, 2009)&lt;br /&gt;
 &lt;br /&gt;
====2.3.1.1	Community Assessment Steps====&lt;br /&gt;
* Identify specific community problems that stand in the way of meeting community goals. Produce a community problem statement,&lt;br /&gt;
* Creates a work plan for addressing problems and attaining the goals, &lt;br /&gt;
* Describe measurable beneficial impacts to the community that result from the project’s implementation, &lt;br /&gt;
* Determine the level of resources or funding necessary to implement the project.&lt;br /&gt;
* Solicit community social economic assessment report from Local Government Authorities for use in choice of technology to achieve project sustainability&lt;br /&gt;
&lt;br /&gt;
====2.3.1.2	 Methods of conducting community assessment====&lt;br /&gt;
Two methods can be employed for conducting community assessment. They are comprehensive and strategic planning.&lt;br /&gt;
&lt;br /&gt;
=====2.3.1.2.1	Comprehensive community assessment=====&lt;br /&gt;
This process should involve:&lt;br /&gt;
* Completing a community-wide needs assessment to engage the community in identifying and prioritizing all long-range goals and the community problems preventing the achievement of those goals, &lt;br /&gt;
* Next, the community is involved in the process of developing a method to accomplish long-range goals,  &lt;br /&gt;
* Discussing initial ways to overcome the problems &lt;br /&gt;
* Develop measures to monitor progress towards achieving those goals. &lt;br /&gt;
&lt;br /&gt;
Comprehensive plans require at least a year to complete and should cover a five- to ten-year time span. &lt;br /&gt;
&lt;br /&gt;
======2.3.1.2.2	Strategic community assessment======&lt;br /&gt;
This is a process used when a community or an organization already has a comprehensive plan and wants to move forward to achieve its long-range goals. Strategic planning involves:&lt;br /&gt;
Participation of the community in identifying problems that stand between the community and its goals and to move the community towards realizing its long-range vision. &lt;br /&gt;
&lt;br /&gt;
The product of strategic planning, simply called the “strategic plan,” builds on pre-established long-range goals by designing projects related to one or more of these goals. A strategic plan generally takes at least six months to complete.&lt;br /&gt;
&lt;br /&gt;
===2.3.2	Pre-feasibility Study===&lt;br /&gt;
The pre-feasibility study stage involves initial fieldwork and studies of alternative water resource development plans. The report issued is an outline of possibilities and a list of all the fieldwork activities that need to be accomplished at a feasibility study or even a preliminary engineering design stage.&lt;br /&gt;
&lt;br /&gt;
The objective of this initial study is to determine whether it is worthwhile to proceed with more detailed investigations. In other words at this stage, various projects or alternatives are screened and this should normally reduce the number of options considered feasible to no more than three or so. The report should, however, contain recommendations on the proposed project and how to proceed with the detailed investigations.&lt;br /&gt;
&lt;br /&gt;
These should include indications on the following:&lt;br /&gt;
&lt;br /&gt;
* Data to be collected,&lt;br /&gt;
* Remaining alternatives to be considered and investigated,&lt;br /&gt;
* Professional human resources required,&lt;br /&gt;
* Estimate of time that will be taken or needed,&lt;br /&gt;
* Budgetary financial requirements.&lt;br /&gt;
&lt;br /&gt;
The above are considered taking into account:&lt;br /&gt;
&lt;br /&gt;
* Long term needs,&lt;br /&gt;
* Deficiencies in the existing system (if any),&lt;br /&gt;
* Phases of project implementation.&lt;br /&gt;
&lt;br /&gt;
Briefly, the pre-feasibility report should give an outline of the future development, which seems most appropriate to provide the project area with water in the long term. The other major aim may be to select a short-term project that may be implemented to overcome any immediate needs (crash programme) while the long-term project is being prepared. &lt;br /&gt;
&lt;br /&gt;
===2.3.3	Feasibility Study===&lt;br /&gt;
The feasibility study stage develops the pre-feasibility work further and ends with a Report which normally concentrates on the project alternatives that were recommended for more detailed consideration at the pre-feasibility stage.&lt;br /&gt;
&lt;br /&gt;
The study has to be carried out by a team of competent and experienced personnel from the Ministry, RUWASA and WWSA or with the help of a private sector. At this stage, the following should be achieved:&lt;br /&gt;
&lt;br /&gt;
* Collection of sufficient design data,&lt;br /&gt;
* Appraise the alternatives,&lt;br /&gt;
* Alternative plans (projects) adequately studied and evaluated,&lt;br /&gt;
* Socio-economic analysis adequately conducted and completed&lt;br /&gt;
* Solicit the views and preferences with community in an open meeting&lt;br /&gt;
* Discuss the merits and demerits with community representatives&lt;br /&gt;
* Rank alternatives on the basis of appropriate costing method and perceived ability of community to afford the costs of operation and maintenance and reach agreement in principle with concerned water officials.&lt;br /&gt;
* Inform the community reasons for selection of the alternative(s) and seek their agreement and approval.&lt;br /&gt;
* Conduct Environmental Impact assessment (EIA). For larger projects a statement on Life Cycle Assessment should be included indicating the extent of quantitative and other relevant information currently available,&lt;br /&gt;
* Preliminary engineering design done, including a review of alternative materials,&lt;br /&gt;
* Preliminary cost estimates done,&lt;br /&gt;
* Economic internal rate of return and financial internal rate of return,&lt;br /&gt;
* Carry out design to a level sufficient to enable construction to proceed either using local (District) based contractors or a Force Account approach using local sub-contractors as considered feasible and appropriate,&lt;br /&gt;
* Most feasible project (least cost) selected, &lt;br /&gt;
* Feasibility report prepared and presented to the authorities for approval&lt;br /&gt;
&lt;br /&gt;
The report may also include interim progress reports, appendices of data collected during the detailed study. The feasibility report should be presented as a supporting document to apply for financing from the financing agencies.&lt;br /&gt;
====2.3.3.1	 Water Supply Projects Ranking and Technology Selection Criteria====&lt;br /&gt;
=====2.3.3.1.1	Ranking of Projects=====&lt;br /&gt;
Projects to be implemented should be ranked on the basis of the following criteria;&lt;br /&gt;
* Type of technology,&lt;br /&gt;
* Quantity of water,&lt;br /&gt;
* ESIA Report comments,&lt;br /&gt;
* Negative environment impact,&lt;br /&gt;
* Quality of water available,&lt;br /&gt;
* Cost/benefit analysis, &lt;br /&gt;
* Walking distance scheme complexity.&lt;br /&gt;
&lt;br /&gt;
=====2.3.3.1.2	Choice of Technology=====&lt;br /&gt;
As far as possible ranking of project selection is concerned, technology choice should be based on progressive consideration of:&lt;br /&gt;
* Hand pump(s) from proven permanent deep hand dug well(s) or shallow borehole(s),&lt;br /&gt;
* Gravity scheme from protected spring,&lt;br /&gt;
* Medium or deep well with appropriate hand pump (rotary type),&lt;br /&gt;
* Pumped / Piped Scheme Electrical Driven,&lt;br /&gt;
* Pumped/Piped Scheme Solar Driven.&lt;br /&gt;
&lt;br /&gt;
For point water sources or simple distribution systems, a prime location for a domestic point should be the village primary school followed by a village health facility (if any). Provision of improved sanitation and hand washing facilities at both primary school and health facility should also receive priority consideration in any village scheme. Use the relevant WASH guidelines for design of the washing facilities.&lt;br /&gt;
&lt;br /&gt;
===2.3.4	Preliminary and Detailed Design===&lt;br /&gt;
After the feasibility report is presented and approved, the preliminary and the preferred alternative should be selected and the finances sought. The following should be considered while conducting the design:&lt;br /&gt;
* The Engineer should prepare the preliminary engineering design and then the detailed or final project report,  &lt;br /&gt;
* These reports should provide the basis for implementation,  &lt;br /&gt;
* The initial report has to provide the design basics which are then developed further in the detailed design of the project including working drawings and tender documents,  &lt;br /&gt;
* They should however include a review of all relevant aspects of this DCOM Manual and either accept or otherwise indicate, complete with detailed reasoning, why different criteria is proposed. &lt;br /&gt;
&lt;br /&gt;
In addition, the report should address the following:&lt;br /&gt;
* The issue of costing being adopted and requirement for extent of whole life cycle analysis and adaptation of costing,  &lt;br /&gt;
* Consideration of the environmental impacts of the project and its envisaged elements,  &lt;br /&gt;
* Issue of climate change and its possible effects on the project being designed. &lt;br /&gt;
&lt;br /&gt;
It should be noted that the conceptual designs provided at the feasibility study or preliminary engineering stages are generally inadequate for the construction of the project. Foremost, the Engineer arranges for any outstanding detailed field investigations, surveys and data collection. Based on the detailed field data collected; detailed designs, plans and estimates are prepared.&lt;br /&gt;
&lt;br /&gt;
Detailed designs should include:&lt;br /&gt;
* Statistical analysis of data collected for the population and demand projections; hydrological ,hydrogeological  and meteorological data,&lt;br /&gt;
* Least cost lay-outs for different components of the project, i.e. treatment plants, hydraulic and structural works,&lt;br /&gt;
* Structural and stability computations of different structures,&lt;br /&gt;
* Calculations for pumps, motors, power generators and other machinery and equipment,&lt;br /&gt;
* Engineering analysis for deciding the most economic size of delivery mains.&lt;br /&gt;
* Hydraulic computations for the distribution system,&lt;br /&gt;
* Bills of quantities.&lt;br /&gt;
* Detailed design should include the following:&lt;br /&gt;
&lt;br /&gt;
====2.3.4.1	Detailed Engineering Drawings====&lt;br /&gt;
These should include:&lt;br /&gt;
&lt;br /&gt;
* Index plan showing overall layout of the project,&lt;br /&gt;
* Schematic diagram showing levels of salient components of the project (may not necessarily be to scale),&lt;br /&gt;
* Detailed plans and sections in scale for the headwords, treatment plants, clear water storage tank, pumping station, in a scale 1:20 to 1:100 depending on the details and size of the works,&lt;br /&gt;
* Detailed structural plans for structures, intake, treatment plant, clear water reservoir etc., in a scale of 1:20,&lt;br /&gt;
* Index plan of the distribution system normally in an appropriate scale,&lt;br /&gt;
* Longitudinal sections of the delivery main and details of appurtenances in scales: Horizontal scale 1:500 to 1:5000 depending on distance and details Vertical scale 1:20 to 1:100 depending on the terrain surface undulations.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.2		Detailed estimates of capital costs====&lt;br /&gt;
Project cost estimates should be based on unit costs derived from recent projects of a similar magnitude, complexity and remoteness from or proximity to ports or major urban areas.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.3	 Detailed estimates of recurrent costs====&lt;br /&gt;
As far as possible this should be based on unit costs provided by the operating authority or from schemes of a similar size and nature.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.4	 Anticipated revenue====&lt;br /&gt;
These should be based on the recommendations made regarding tariff structures or provided by the operating authority or regulator.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.5	 Detailed design report====&lt;br /&gt;
A report should accompany the detailed designs, plans and estimates elaborating on the:&lt;br /&gt;
* Engineering aspects,&lt;br /&gt;
* Financial aspects,&lt;br /&gt;
* Administrative aspects, &lt;br /&gt;
* Tender documents &lt;br /&gt;
* Specifications.&lt;br /&gt;
&lt;br /&gt;
====2.3.4.6	 Project write-up to be submitted to potential financiers====&lt;br /&gt;
Each Development Partner may have a different pattern of project presentation for financial request. The project document should therefore follow more guidelines as indicated by the financiers or the local funding sources where applicable.&lt;br /&gt;
&lt;br /&gt;
====2.3.5	Project Phasing====&lt;br /&gt;
Sometimes the implementation of a project is carried out in phases due to among other things, the following reasons:&lt;br /&gt;
* Financial resources available,&lt;br /&gt;
* Opportunity cost of money,&lt;br /&gt;
* Economies of scale,&lt;br /&gt;
* Growth rate in the area,&lt;br /&gt;
* Rate of development in the area,&lt;br /&gt;
* The design (working) life of various installations,&lt;br /&gt;
* Development in levels of service,&lt;br /&gt;
* New technology or method that needs piloting before rolling it out&lt;br /&gt;
Once the basic design period is decided (usually between 10 and 20 years) and water demand is computed for different years, the different elements can be phased. Exceptions do occur where financial assistance capital is being used and there is fear or a probability that further trunches will not be available just a few years later.&lt;br /&gt;
&lt;br /&gt;
Generally, phasing should be undertaken as follows: &lt;br /&gt;
(i)	Dams, river and spring intakes, should be implemented in a single phase to cover all of the ultimate design demand or the hydrologically calculated water availability. This is particularly significant for dams as flood spillways form an expensive integral part and the need to raise a spillway inlet and deal with the additional energy at its exit is usually very costly.&lt;br /&gt;
(ii)	Boreholes to be constructed in Multiple Phases according to the growth in demand.&lt;br /&gt;
(iii)	Treatment plants and storage tanks to be constructed stepwise or in phases, according to the projected growth in demand.&lt;br /&gt;
(iv)	Mechanical installations to be implemented in Multiple Phases according to the design life of the equipment.&lt;br /&gt;
(v)	Pump houses constructed in a Single Phase with space for additional mechanical plant.&lt;br /&gt;
(vi)	Rising mains and main conduits between units to be constructed to cover the ultimate demand in a single Phase.&lt;br /&gt;
(vii)	Long transmission mains to be constructed as two parallel lines in a single Phase where funds allow or in Two Phases where not. It can be advantageous to dedicate one of two parallel transmission mains to supplying water to the terminal reservoir whilst using the second for a mix of local distribution (daytime) and conveyance to the terminal reservoir (night time).&lt;br /&gt;
(viii)	Distribution systems to be constructed according to the growth in development in Multiple Phases.&lt;br /&gt;
&lt;br /&gt;
===2.3.6	Procurement===&lt;br /&gt;
====2.3.6.1	Preparation of Tender Documents====&lt;br /&gt;
The Procurement Management Unit (PMU) using the approved templates as guided by PPRA documentation undertakes preparation of tender documents. In preparing the tender documents undertaken by PMU, unit rate contract is normally adopted for project components such as intake, delivery mains, distribution system, storage tanks and other appurtenances. For specialized areas like the treatment plants and pumping stations it may be necessary to prepare separate tenders for the supply and installation of such facilities. The superstructure may still be included in the main contract bill of quantities. As much as possible one contract is preferred. The suppliers of such specialized equipment would then be included as sub-contractors of the main contractor. Important documents included in contract documents includes:&lt;br /&gt;
* Letter of Invitation to Tender &lt;br /&gt;
* Instruction to Tenderers &lt;br /&gt;
* General Conditions of Contract&lt;br /&gt;
* Special Conditions of Contract&lt;br /&gt;
* Drawings &lt;br /&gt;
* Specifications &lt;br /&gt;
* Bills of Quantities&lt;br /&gt;
* Tender Forms&lt;br /&gt;
* Security Forms &lt;br /&gt;
* Anti-bribery Pledge&lt;br /&gt;
* Schedule of Additional Information&lt;br /&gt;
* Information Data&lt;br /&gt;
&lt;br /&gt;
====2.3.6.2	Tendering process====&lt;br /&gt;
This process involves use of public procurement act to select service providers as detailed in following steps; &lt;br /&gt;
* Issue of tender documents&lt;br /&gt;
* Submission and receipt of tenders&lt;br /&gt;
* Opening of tenders&lt;br /&gt;
* Evaluation of tenders&lt;br /&gt;
* Award of tender&lt;br /&gt;
* Signing of contract agreement&lt;br /&gt;
&lt;br /&gt;
===2.3.7	Implementation/Construction Stage===&lt;br /&gt;
Construction stage includes contract management, Contract supervision and administration.&lt;br /&gt;
====2.3.7.1	Contract Management====&lt;br /&gt;
Contract management entails the following;&lt;br /&gt;
* Contract Management Plan (CMP),&lt;br /&gt;
* Contract Delivery Follow-up,&lt;br /&gt;
* Work progress monitoring &amp;amp; control,  &lt;br /&gt;
* All projects executed must have a completion report (as constructed built reports and drawings). It is essential that Engineers or Foremen keep an up to date record of all project activities including all changes to the original design with reasons for this clearly indicated as well as the approving authority.&lt;br /&gt;
* Initial and Final Acceptance of the Works&lt;br /&gt;
* Contract Close Out&lt;br /&gt;
====2.3.7.2	Contract supervision and administration ====&lt;br /&gt;
During construction stage, it is necessary to consider the following;&lt;br /&gt;
* Each phase of the project implementation should be planned in detail using techniques such as the Critical Path Method (CPM) or Programme Evaluation or/and Review Technique (PERT ) to ensure time control,&lt;br /&gt;
* Work together with the Contractor to prepare a Quality Assurance Plan which shall narrate the scope of the works and the expected quality requirements for the project, the role of the participants in ensuring quality requirements are met&lt;br /&gt;
* Obtain a cash flow forecast from the contractor, and make the Client aware of his payment obligations based on the forecast&lt;br /&gt;
* Keep a close track of all contractors approved claims and adjust the contract price to reflect increase or decrease in the contract price&lt;br /&gt;
* Detailed information in procurement, contract management, contract supervision and administration is detailed well in chapter three and four of Volume III Construction Supervision for Water Supply and Sanitation Projects.&lt;br /&gt;
&lt;br /&gt;
===2.3.8	Operation and Maintenance Stage===&lt;br /&gt;
   This process takes over after the project completion, it involves;&lt;br /&gt;
* Preparation of O&amp;amp;M Plan,&lt;br /&gt;
* Development of Individual Unit Plans for O&amp;amp;M,&lt;br /&gt;
* Plan for capacity Building of O&amp;amp;M Personnel,&lt;br /&gt;
* Plan for Providing Spares and Tools,&lt;br /&gt;
* Plan for Water Audit and Leakage Control,&lt;br /&gt;
* Plan for Efficient Use of Power,&lt;br /&gt;
* Plan for sound financial management system,&lt;br /&gt;
* Plan for Information Education Communication for Water and Sanitation Services,&lt;br /&gt;
* Reports and Record Keeping,&lt;br /&gt;
* Develop appropriate maintenance schedule and check lists,&lt;br /&gt;
* Utilize Standard Operating Procedures,&lt;br /&gt;
* Utilize Water Safety Plans.&lt;br /&gt;
&lt;br /&gt;
Detailed information on planning for operation and maintenance is found in chapter three and four of Volume IV Operation and Maintenance of Water Supply and Sanitation Projects&lt;br /&gt;
&lt;br /&gt;
===2.3.9	Performance Monitoring===&lt;br /&gt;
The aim of the project is to provide the services uninterrupted. To ensure this, a proper monitoring mechanism of the performance of the project should be prepared. Such a mechanism could include proper procedures for procurement and distribution of spare parts, fuel, replacement, a maintenance programme for the project including personnel at the village, District and if necessary at Regional and National levels also. Likewise a water quality surveillance procedure should be instituted in the framework of the existing mechanism.&lt;br /&gt;
&lt;br /&gt;
==2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans==&lt;br /&gt;
It is imperative that during planning of the water supply and sanitation project, designer should consult the Integrated Water Resources Management and Development (IWRMD) plan for a basin where the project is planned to be executed. The development of an IWRMD Plan is a key objective of the water resources component of the Water Sector Development Programme 2006-2025. It is a legal requirement provided for in the Water Resources Management Act, No. 11 of 2009. The plan provides a blueprint for sustainable development and management of the basin’s water resources. &lt;br /&gt;
&lt;br /&gt;
Thus, a water supply and sanitation project designer is advised and encouraged to consult IWRMD plans as they provide:&lt;br /&gt;
&lt;br /&gt;
* The status of water resource availability (both quantity and quality) in the basin,&lt;br /&gt;
* Water data and information necessary for the design of the projects,&lt;br /&gt;
* Framework for water allocations among its competing demands,&lt;br /&gt;
* Water demand for water related sectors,&lt;br /&gt;
* Stakeholders consultation plan.&lt;br /&gt;
&lt;br /&gt;
===2.4.1	Status of Development and Implementation of IWRMD Plans===&lt;br /&gt;
By the time of development of this DCOM manual, IWRMD plans had been developed for six (6) out of the nine basins. The six basins are:&lt;br /&gt;
* Rufiji River Basin,&lt;br /&gt;
* Ruvuma and Southern Coast Basin,&lt;br /&gt;
* Lake Tanganyika Basin,&lt;br /&gt;
* Lake Nyasa Basin,&lt;br /&gt;
* Internal Drainage and&lt;br /&gt;
* Lake Rukwa Basin&lt;br /&gt;
&lt;br /&gt;
It was reported that the development of IWRMD plans for Lake Victoria Basin and Wami/Ruvu basins were on-going. &lt;br /&gt;
&lt;br /&gt;
IWRMD plans implementation challenges have been observed in some basins. These include:&lt;br /&gt;
&lt;br /&gt;
* Inadequate funding to implement plans recommendations,&lt;br /&gt;
* Some plans are not implementable because of including unrealistic recommendations,&lt;br /&gt;
* Some plans are considered to have been more of studies rather than plans,&lt;br /&gt;
* Inadequate human resources capacity to implement them,&lt;br /&gt;
* As required by EMA, ESIAs have not been conducted, contrary to the requirement&lt;br /&gt;
&lt;br /&gt;
===2.4.2	Components of IWRMD Plans===&lt;br /&gt;
The developed IWRMD plans are expected to have the following main components:&lt;br /&gt;
* Component 1: Inventory and review of water availability, use and demand,&lt;br /&gt;
* Component 2: Institutional, Policy and legal framework,&lt;br /&gt;
* Component 3: Sector/Thematic Water Plans,&lt;br /&gt;
* Component 4: Integrated Water Resources Management and Development Plan, &lt;br /&gt;
* Component 5: IWRMD Plan Implementation Strategy and Action Plan.&lt;br /&gt;
&lt;br /&gt;
The production capacity of a source is very important in planning a water supply system. An estimate of the water that can be reliably produced by a water source like a well or spring gives the planner a basis to decide for or against its development. For the source(s) to be considered adequate, they must at least satisfy the maximum daily demand of the area to be served.&lt;br /&gt;
&lt;br /&gt;
==2.5		Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change ==&lt;br /&gt;
&lt;br /&gt;
Water Safety Plan (WSP) is the most effective means of consistently ensuring the safety of a drinking-water supply through the use of a comprehensive risk assessment and risk management approach that encompasses all steps in water supply from the catchment to the consumer (WHO, 2017). The approach enables the operators and managers of water utilities to know the system thoroughly, identify where and how problems could arise, put multiple barriers and management systems in place to stop the problems before they happen and making all parts of the system work properly so as to ensure the safety and acceptability of a drinking water supply intended for human consumption and other domestic uses as summarized in the WHO safe water chain frameworks.&lt;br /&gt;
&lt;br /&gt;
Thus, during the planning phase, a designer should consult guidelines for the preparation of Water Safety Plans - Resilient to Climate Change, which has been prepared and published by Ministry of Water (MoW, 2015)&lt;br /&gt;
&lt;br /&gt;
==2.6	Environmental and Social Impact Assessment Compliance==&lt;br /&gt;
Section 81 of the Environmental Management Act (Cap 191) requires all developers of projects identified in the 3rd Schedule of the Act and detailed in the 1st Schedule of the Environmental Management (Environmental Impact Assessment And Audit) (Amendment) Regulations, 2018, to undertake Environmental Impact Assessment (EIA). Section 82 of EMA (Cap 181) requires that the EIA be carried out prior to the commencement or financing of the project. Procedures for carrying out the EIA, identified under the EIA and Audit  (Amendment) Regulations of 2018 identify eight steps to be followed. According to EIA and Audit (Amendment) Regulations of 2018, projects are classified into the following categories, namely:&lt;br /&gt;
&lt;br /&gt;
(a) “A” category for Mandatory projects;&lt;br /&gt;
 (b) “B1” category for Borderline Project;&lt;br /&gt;
(c) “B2” category for Non-Mandatory; and&lt;br /&gt;
(d) “Special Category&lt;br /&gt;
&lt;br /&gt;
So it is imperative that a proponent and developer of any water supply and sanitation project categorizes their project prior to actual project implementation for the same.&lt;br /&gt;
&lt;br /&gt;
===2.6.1	Procedures for Conducting ESIA in Tanzania===&lt;br /&gt;
Procedures for carrying out the ESIA, identified under the EIA and Audit (Amendment) Regulations of 2018 identify eight key steps to be followed in the EIA process in Tanzania. These are:&lt;br /&gt;
&lt;br /&gt;
* Step 1: Registration,&lt;br /&gt;
* Step 2: Screening, &lt;br /&gt;
* Step 3: Scoping,&lt;br /&gt;
* Step 4: Environmental Assessment,&lt;br /&gt;
* Step 5: Review,&lt;br /&gt;
* Step 6: Recommendations of the Technical Advisory Committee (TAC),&lt;br /&gt;
* Step 7: Submission To The Minister For Environment,&lt;br /&gt;
* Step 8: Approval of the EIS.&lt;br /&gt;
&lt;br /&gt;
It is recommended to consult NEMC guidelines and Environmental Management (Environmental Impact Assessment And Audit) (Amendment) Regulations, 2018 for more details. Also, the following Ministry of Water guidelines, accessible at have to be consulted.&lt;br /&gt;
a)	Guidelines of Good Environmental and Social Practices (GGESP) of July 2019,&lt;br /&gt;
b)	Environmental and Social Management Framework (ESMF) of July 2019.&lt;br /&gt;
&lt;br /&gt;
===2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance===&lt;br /&gt;
&lt;br /&gt;
Section 105 part (2) of the Environmental Act requires that wherever there is a major water project planned for construction, the Ministry responsible for water should conduct Strategic Environmental and Social Assessment. The strategic environmental assessment shall asses the area marked for development and include:&lt;br /&gt;
&lt;br /&gt;
* Baseline environmental conditions and status of natural resources,&lt;br /&gt;
* Identification of ecological sensitive and protected areas,&lt;br /&gt;
* Identification and description of communities around the area,&lt;br /&gt;
* Existing social-economic conditions,&lt;br /&gt;
* Existing economic activities and infrastructure.&lt;br /&gt;
The strategic environmental and social assessment shall be submitted to the Minister responsible for Environment for approval before the planning process.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
==2.7	Potential Impacts of Climate Change on Water Supply Projects==&lt;br /&gt;
It should be emphasized that immediately the project is conceived, hydrological, rainfall and other meteorological data collection must be initiated. In addition and given the long design life of such structures, consideration must be given to the possible impacts of climate change. Detailed account of predictions and impacts of climate change on water supply projects is provided in Appendix A.&lt;br /&gt;
&lt;br /&gt;
URT (2019) has recommended strategies and plans to adapt risks from climate change. The design related strategies of infrastructure, which a designer should consider while planning for water supply projects include:&lt;br /&gt;
&lt;br /&gt;
* Where possible, have at least two sources of supply at different locations. Build superstructures above high flood-line level.&lt;br /&gt;
* Adopt energy-efficiency programmes and, where possible, select facilities which require less power consumption.&lt;br /&gt;
* Monitor wells near coastlines to prevent salinization. If climate change causes sea levels to rise dramatically, even aquifers that have been sustainably utilized can suffer salinization.&lt;br /&gt;
* Utilize renewable energy sources.&lt;br /&gt;
&lt;br /&gt;
Guidelines for resiliency to climate change for urban water supply utilities have been published by the Ministry of Water. &lt;br /&gt;
&lt;br /&gt;
==2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages==&lt;br /&gt;
As explained in detail in section 2.1 of this volume, the CBWSOs have to  be involved in the complete life cycle of the project including ensuring their sustainability during operation and maintenance of the projects under the overall coordination of WSSAs and RUWASA.&lt;br /&gt;
&lt;br /&gt;
==2.9	References==&lt;br /&gt;
Asadieh, B. and Krakauer, N.Y. (2016). Impacts of changes in precipitation amount and distribution on water resources studied using a model rainwater harvesting system. J. Am. Water Resour. Assoc. 52: 1450–1471.https://doi.org/10.1111/ 1752-1688.12472.&lt;br /&gt;
&lt;br /&gt;
Gebrechorkos, S. H., Hülsmann, S., &amp;amp; Bernhofer, C. (2019). Regional climate projections for impact assessment studies in East Africa. Environmental Research Letters, 14(4), 044031. https://doi.org/10.1088/1748-9326/ab055a&lt;br /&gt;
&lt;br /&gt;
Giannini, A., M. Biasutti, I. Held, and A. Sobel (2008). A global perspective on African climate. Clim. Change, 90: 359–383.&lt;br /&gt;
&lt;br /&gt;
Hansingo, K., and C. Reason (2008). Modelling the atmospheric response to SST dipole patterns in the South Indian Ocean with a regional climate model. Meteorol. Atmos. Phys., 100: 37–52.&lt;br /&gt;
&lt;br /&gt;
Hansingo, K., and C. Reason (2009). Modelling the atmospheric response over southern Africa to SST forcing in the southeast tropical Atlantic and southwest subtropical Indian Oceans. Int. J. Climatol., 29: 1001–1012.&lt;br /&gt;
&lt;br /&gt;
Hermes, J., and C. Reason (2009). Variability in sea-surface temperature and winds in the tropical south-east Atlantic Ocean and regional rainfall relationships. Int. J. Climatol., 29: 11–21.&lt;br /&gt;
&lt;br /&gt;
IPCC (2007). Summary for policymakers Climate Change 2007: Impacts, Adaptation and Vulnerability. Contribution of Working Group II to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change ed M L Parry, O F Canziani, J P Palutikof, P J van der Linden and C E Hanson (Cambridge: Cambridge University Press) pp 7-22.&lt;br /&gt;
&lt;br /&gt;
IPCC (2014). Climate Change 2014: Summary for Policymakers, Synthesis Report. Contribution of Working Groups I, II and III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change [Core Writing Team, R.K. Pachauri and L.A. Meyer (eds.)]. IPCC, Geneva, Switzerland, 151 pp.&lt;br /&gt;
&lt;br /&gt;
Li, J., Chen, Y.D., Gan, T.Y., Lau, N. (2018). Elevated increases in human-perceived temperature under climate warming. Nat. Clim. Chang. 8: 43–47. https://doi.org/10.1038/s41558-017-0036-2.&lt;br /&gt;
&lt;br /&gt;
Marchant, R., C. Mumbi, S. Behera, and T. Yamagata (2007). The Indian Ocean dipole—the unsung driver of climatic variability in East Africa. Afr. J. Ecol., 45: 4–16.&lt;br /&gt;
&lt;br /&gt;
Moss, R. H. et al. (2010). The next generation of scenarios for climate change research and assessment. Nature, Vol 463, 11 February 2010, doi:10.1038/nature08823.&lt;br /&gt;
&lt;br /&gt;
Pohl, B., N. Fauchereau, C. Reason, and M. Rouault (2010). Relationships between the Antarctic Oscillation, the Madden - Julian Oscillation, and ENSO, and Consequences for Rainfall Analysis. J. Clim., 23: 238–254.&lt;br /&gt;
&lt;br /&gt;
Rouault, M., P. Florenchie, N. Fauchereau, and C. Reason (2003). South East tropical Atlantic warm events and southern African rainfall. Geophys. Res. Lett., 30, doi:10.1029/2002GL014840.&lt;br /&gt;
&lt;br /&gt;
UNFCCC (2010). The Cancun Agreements. United Nations Framework Convention on Climate Change http://unfccc.int/meetings/cancunnov2010/meeting/6266.php, 2010.&lt;br /&gt;
&lt;br /&gt;
URT (2019). Water sector development programme. Environmental and social management framework (ESMF). Revised version. Ministry of Water.&lt;br /&gt;
&lt;br /&gt;
Vautard, R., Gobiet, A., Sobolowski, S., Kjellström, E., Stegehuis, A., Watkiss, P., Mendlik. T., Landgren, O., Nikulin, G., Teichmann, C. and Jacob, D. (2014). The European climate under a 2°C global warming. Environ. Res. Letters. Environ. Res. Lett. 9, 034006, doi:10.1088/1748-9326/9/3/034006.&lt;br /&gt;
&lt;br /&gt;
Vigaud, N., Y. Richard, M. Rouault, and N. Fauchereau (2009). Moisture transport between the South Atlantic Ocean and southern Africa: Relationships with summer rainfall and associated dynamics. Clim. Dyn., 32: 113–123.&lt;br /&gt;
&lt;br /&gt;
WHO (2017). Climate-resilient water safety plans: Managing health risks associated with climate variability and change. World Health Organization. ISBN: 978-92-4-151279-4. Retrieved from: https://www.who.int/water_sanitation_health/publications/climate-resilient-water-safety-plans/en/&lt;br /&gt;
&lt;br /&gt;
Previous Page: [[Chapter One: Introduction|Chapter One: Introduction]] &amp;lt;&amp;lt;  &amp;gt;&amp;gt; Next Page: [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]]&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=Chapter_Two:_Project_Planning&amp;diff=513</id>
		<title>Chapter Two: Project Planning</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=Chapter_Two:_Project_Planning&amp;diff=513"/>
		<updated>2020-03-31T10:33:57Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;Arguably, planning of water supply projects is considered to be one of the most important stages in the design. Thus, it is strongly advised and emphasized that much time should be spent to undertake proper project planning. A proper project planning will ensure effective and efficient completion of the project successfully. In this chapter, project planning is presented in seven parts that are detailed below. These include:&lt;br /&gt;
&lt;br /&gt;
* Planning considerations for water supply projects&lt;br /&gt;
* Project Planning steps&lt;br /&gt;
* Consulting the Integrated Water Resources Management and Development Plan&lt;br /&gt;
* Consult guideline for preparation of Water Safety Plan – resilient to climate change.&lt;br /&gt;
* Environmental and Social Impact Assessment (ESIA) and Strategic Environmental and Social Impact Assessment (SESIA) Compliance&lt;br /&gt;
* Potential Impacts of Climate Change on Water Supply Projects&lt;br /&gt;
* Participation of CBWSOs in Project Planning Stages&lt;br /&gt;
&lt;br /&gt;
=Chapter Two: Project Planning=&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
2.1	Planning Considerations for Water Supply Projects &lt;br /&gt;
Before commencement of any development of a water project, it is essential to conduct project planning. Planning is a process that should entail the following:&lt;br /&gt;
•	Undertake ESIA and SESIA studies,&lt;br /&gt;
•	Engagement and involvement of the local community to instill the ownership, provide the local knowledge, project buy in and accommodate community needs and requirements,&lt;br /&gt;
•	Assess safe and reliable yield or discharge and quality of water source,&lt;br /&gt;
•	Determination of the system layout,&lt;br /&gt;
•	Conduct design of the water supply project,&lt;br /&gt;
•	Implement the project in terms of construction, operation and maintenance,&lt;br /&gt;
•	Work out to obtain a sound and robust project financing.&lt;br /&gt;
&lt;br /&gt;
It should be emphasized and stressed that collection of good quality, reliable, credible and enough data should be given high priority at all stages of project implementation. Population projection methods and their relevance for rural and urban settings or areas as recommended by the National Bureau of Statistics (NBS) have to be evaluated. Demographic features such as social and economic conditions have to be studied before design projections can be established. Also, water source reliability should be carried out before any further stage of project implementation.&lt;br /&gt;
2.2	Project Planning Steps&lt;br /&gt;
Project planning involves a series of steps that determine how project goals will be achieved. The goals may be solicited from the existing community or a strategic plan. In an event that there is not any plan, project plans can be developed through community meetings and gatherings, councils or board meetings, special focused group discussions or other planning processes. &lt;br /&gt;
&lt;br /&gt;
The main steps of project planning include:&lt;br /&gt;
Step 1: Initiation&lt;br /&gt;
Step 2: Pre-feasibility study&lt;br /&gt;
Step 3: Feasibility study&lt;br /&gt;
Step 4: Preliminary and Detailed Design&lt;br /&gt;
Step 5: Project phasing&lt;br /&gt;
Step 6: Procurement&lt;br /&gt;
Step 7: Implementation/Construction&lt;br /&gt;
Step 8: Operation and Maintenance (Management)&lt;br /&gt;
Step 9: Performance Monitoring&lt;br /&gt;
&lt;br /&gt;
The planning of water supply projects can be represented diagrammatically by a step wise planning cycle as shown in Figure 2.1.&lt;br /&gt;
&lt;br /&gt;
2.3	Pump Protection&lt;br /&gt;
The following sections provide a brief description of each of the twelve project planning steps.&lt;br /&gt;
&lt;br /&gt;
2.3.1	Initiation&lt;br /&gt;
Initiation or sometimes referred to as triggering stage, is a step where initial ideas of the project are presented. Community mobilization through awareness raising is conducted at this stage. The whole idea is to inform the community on the start of the project, solicit community input and knowledge about the project area. Project common understanding is also expected to be realized at this step. &lt;br /&gt;
&lt;br /&gt;
The outcome of this stage of planning is to acquire an understanding of the community conditions and identify problems that prevent the community from achieving its long-range goals. Community conditions which must be collected includes aspects of the community such as: &lt;br /&gt;
* Its geographic location, &lt;br /&gt;
* Demographics, &lt;br /&gt;
* Ecosystem, &lt;br /&gt;
* History,e.t.c&lt;br /&gt;
&lt;br /&gt;
The data collection for the above information should employ community assessment methods.&lt;br /&gt;
&lt;br /&gt;
[[File:Volume I Figure 2.1 Projects Planning Process.png|thumb|Figure 2.1: Projects Planning Process]]&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
(Source: Modified after Design Manual 3rd edition, 2009)&lt;br /&gt;
 &lt;br /&gt;
2.3.1.1	Community Assessment Steps&lt;br /&gt;
•	Identify specific community problems that stand in the way of meeting community goals. Produce a community problem statement,&lt;br /&gt;
•	Creates a work plan for addressing problems and attaining the goals, &lt;br /&gt;
•	Describe measurable beneficial impacts to the community that result from the project’s implementation, &lt;br /&gt;
•	Determine the level of resources or funding necessary to implement the project.&lt;br /&gt;
•	Solicit community social economic assessment report from Local Government Authorities for use in choice of technology to achieve project sustainability&lt;br /&gt;
&lt;br /&gt;
2.3.1.2	 Methods of conducting community assessment&lt;br /&gt;
Two methods can be employed for conducting community assessment. They are comprehensive and strategic planning.&lt;br /&gt;
&lt;br /&gt;
2.3.1.2.1	Comprehensive community assessment&lt;br /&gt;
This process should involve:&lt;br /&gt;
•	Completing a community-wide needs assessment to engage the community in identifying and prioritizing all long-range goals and the community problems preventing the achievement of those goals,&lt;br /&gt;
•	Next, the community is involved in the process of developing a method to accomplish long-range goals, &lt;br /&gt;
•	Discussing initial ways to overcome the problems&lt;br /&gt;
•	Develop measures to monitor progress towards achieving those goals. &lt;br /&gt;
&lt;br /&gt;
Comprehensive plans require at least a year to complete and should cover a five- to ten-year time span. &lt;br /&gt;
&lt;br /&gt;
2.3.1.2.2	Strategic community assessment&lt;br /&gt;
This is a process used when a community or an organization already has a comprehensive plan and wants to move forward to achieve its long-range goals. Strategic planning involves:&lt;br /&gt;
•	Participation of the community in identifying problems that stand between the community and its goals and to move the community towards realizing its long-range vision. &lt;br /&gt;
&lt;br /&gt;
The product of strategic planning, simply called the “strategic plan,” builds on pre-established long-range goals by designing projects related to one or more of these goals. A strategic plan generally takes at least six months to complete.&lt;br /&gt;
&lt;br /&gt;
2.3.2	Pre-feasibility Study&lt;br /&gt;
The pre-feasibility study stage involves initial fieldwork and studies of alternative water resource development plans. The report issued is an outline of possibilities and a list of all the fieldwork activities that need to be accomplished at feasibility study or even preliminary engineering design stage.&lt;br /&gt;
&lt;br /&gt;
The objective of this initial study is to determine whether it is worthwhile to proceed with more detailed investigations. In other words at this stage, various projects or alternatives are screened and this should normally reduce the number of options considered feasible to no more than three or so. The report should however contain recommendations on the proposed project and how to proceed with the detailed investigations.&lt;br /&gt;
&lt;br /&gt;
These should include indications on the following:&lt;br /&gt;
&lt;br /&gt;
•	Data to be collected,&lt;br /&gt;
•	Remaining alternatives to be considered and investigated,&lt;br /&gt;
•	Professional human resources required,&lt;br /&gt;
•	Estimate of time that will be taken or needed,&lt;br /&gt;
•	Budgetary financial requirements.&lt;br /&gt;
&lt;br /&gt;
The above are considered taking into account:&lt;br /&gt;
&lt;br /&gt;
•	Long term needs,&lt;br /&gt;
•	Deficiencies in the existing system (if any),&lt;br /&gt;
•	Phases of project implementation.&lt;br /&gt;
&lt;br /&gt;
Briefly, the pre-feasibility report should give an outline of the future development, which seems most appropriate to provide the project area with water in the long term. The other major aim may be to select a short-term project that may be implemented to overcome any immediate needs (crash programme) while the long-term project is being prepared. &lt;br /&gt;
&lt;br /&gt;
2.3.3	Feasibility Study&lt;br /&gt;
The feasibility study stage develops the pre -feasibility work further and ends with a Report which normally concentrates on the project alternatives that were recommended for more detailed consideration at the pre-feasibility stage.&lt;br /&gt;
&lt;br /&gt;
The study has to be carried out by a team of competent and experienced personnel from the Ministry, RUWASA and WWSA or with the help of a private sector. At this stage the following should be achieved:&lt;br /&gt;
&lt;br /&gt;
•	Collection of sufficient design data,&lt;br /&gt;
•	Appraise the alternatives,&lt;br /&gt;
•	Alternative plans (projects) adequately studied and evaluated,&lt;br /&gt;
•	Socio-economic analysis adequately conducted and completed&lt;br /&gt;
•	Solicit the views and preferences with community in an open meeting&lt;br /&gt;
•	Discuss the merits and demerits with community representatives&lt;br /&gt;
•	Rank alternatives on the basis of appropriate costing method and perceived ability of community to afford the costs of operation and maintenance and reach agreement in principle with concerned water officials.&lt;br /&gt;
•	Inform the community reasons for selection of the alternative(s) and seek their agreement and approval.&lt;br /&gt;
•	Conduct Environmental Impact assessment (EIA). For larger projects a statement on Life Cycle Assessment should be included indicating the extent of quantitative and other relevant information currently available,&lt;br /&gt;
•	Preliminary engineering design done, including a review of alternative materials,&lt;br /&gt;
•	Preliminary cost estimates done,&lt;br /&gt;
•	Economic internal rate of return and financial internal rate of return,&lt;br /&gt;
•	Carry out design to a level sufficient to enable construction to proceed either using local (District) based contractors or a Force Account approach using local sub-contractors as considered feasible and appropriate,&lt;br /&gt;
•	Most feasible project (least cost) selected, &lt;br /&gt;
•	Feasibility report prepared and presented to the authorities for approval&lt;br /&gt;
&lt;br /&gt;
The report may also include interim progress reports, appendices of data collected during the detailed study. The feasibility report should be presented as a supporting document to apply for financing from the financing agencies.&lt;br /&gt;
2.3.3.1	 Water Supply Projects Ranking and Technology Selection Criteria&lt;br /&gt;
2.3.3.1.1	Ranking of Projects&lt;br /&gt;
Projects to be implemented should be ranked on the basis of the following criteria;&lt;br /&gt;
•	Type of technology,&lt;br /&gt;
•	Quantity of water,&lt;br /&gt;
•	ESIA Report comments,&lt;br /&gt;
•	Negative environment impact,&lt;br /&gt;
•	Quality of water available,&lt;br /&gt;
•	Cost/benefit analysis, &lt;br /&gt;
•	Walking distance scheme complexity.&lt;br /&gt;
&lt;br /&gt;
2.3.3.1.2	Choice of Technology&lt;br /&gt;
As far as possible ranking of project selection is concerned, technology choice should be based on progressive consideration of:&lt;br /&gt;
−	Hand pump(s) from proven permanent deep hand dug well(s) or shallow borehole(s),&lt;br /&gt;
−	Gravity scheme from protected spring,&lt;br /&gt;
−	Medium or deep well with appropriate hand pump (rotary type),&lt;br /&gt;
−	Pumped / Piped Scheme Electrical Driven,&lt;br /&gt;
−	Pumped/Piped Scheme Solar Driven.&lt;br /&gt;
&lt;br /&gt;
For point water sources or simple distribution systems, a prime location for a domestic point should be the village primary school followed by a village health facility (if any). Provision of improved sanitation and hand washing facilities at both primary school and health facility should also receive priority consideration in any village scheme. Use the relevant WASH guidelines for design of the washing facilities.&lt;br /&gt;
&lt;br /&gt;
2.3.4	Preliminary and Detailed Design&lt;br /&gt;
After the feasibility report is presented and approved, the preliminary and the preferred alternative should be selected and the finances sought. The following should be considered while conducting the design:&lt;br /&gt;
•	The Engineer should prepare the preliminary engineering design and then the detailed or final project report, &lt;br /&gt;
•	These reports should provide the basis for implementation, &lt;br /&gt;
•	The initial report has to provide the design basics which are then developed further in the detailed design of the project including working drawings and tender documents, &lt;br /&gt;
•	They should however include a review of all relevant aspects of this DCOM Manual and either accept or otherwise indicate, complete with detailed reasoning, why different criteria is proposed. &lt;br /&gt;
&lt;br /&gt;
In addition the report should address the following:&lt;br /&gt;
•	The issue of costing being adopted and requirement for extent of whole life cycle analysis and adaptation of costing, &lt;br /&gt;
•	Consideration of the environmental impacts of the project and its envisaged elements, &lt;br /&gt;
•	Issue of climate change and its possible effects on the project being designed. &lt;br /&gt;
&lt;br /&gt;
It should be noted that the conceptual designs provided at the feasibility study or preliminary engineering stages are generally inadequate for the construction of the project. Foremost, the Engineer arranges for any outstanding detailed field investigations, surveys and data collection. Based on the detailed field data collected; detailed designs, plans and estimates are prepared.&lt;br /&gt;
&lt;br /&gt;
Detailed designs should include:&lt;br /&gt;
•	Statistical analysis of data collected for the population and demand projections; hydrological ,hydrogeological  and meteorological data,&lt;br /&gt;
•	Least cost lay-outs for different components of the project, i.e. treatment plants, hydraulic and structural works,&lt;br /&gt;
•	Structural and stability computations of different structures,&lt;br /&gt;
•	Calculations for pumps, motors, power generators and other machinery and equipment,&lt;br /&gt;
•	Engineering analysis for deciding the most economic size of delivery mains.&lt;br /&gt;
•	Hydraulic computations for the distribution system,&lt;br /&gt;
•	Bills of quantities.&lt;br /&gt;
Detailed design should include the following:&lt;br /&gt;
&lt;br /&gt;
2.3.4.1	Detailed Engineering Drawings&lt;br /&gt;
These should include:&lt;br /&gt;
&lt;br /&gt;
•	Index plan showing overall layout of the project,&lt;br /&gt;
•	Schematic diagram showing levels of salient components of the project (may not necessarily be to scale),&lt;br /&gt;
•	Detailed plans and sections in scale for the headwords, treatment plants, clear water storage tank, pumping station, in a scale 1:20 to 1:100 depending on the details and size of the works,&lt;br /&gt;
•	Detailed structural plans for structures, intake, treatment plant, clear water reservoir etc., in a scale of 1:20,&lt;br /&gt;
•	Index plan of the distribution system normally in an appropriate scale,&lt;br /&gt;
•	Longitudinal sections of the delivery main and details of appurtenances in scales: Horizontal scale 1:500 to 1:5000 depending on distance and details Vertical scale 1:20 to 1:100 depending on the terrain surface undulations.&lt;br /&gt;
&lt;br /&gt;
2.3.4.2		Detailed estimates of capital costs&lt;br /&gt;
Project cost estimates should be based on unit costs derived from recent projects of a similar magnitude, complexity and remoteness from or proximity to ports or major urban areas.&lt;br /&gt;
&lt;br /&gt;
2.3.4.3	 Detailed estimates of recurrent costs&lt;br /&gt;
As far as possible this should be based on unit costs provided by the operating authority or from schemes of a similar size and nature.&lt;br /&gt;
&lt;br /&gt;
2.3.4.4	 Anticipated revenue&lt;br /&gt;
These should be based on the recommendations made regarding tariff structures or provided by the operating authority or regulator.&lt;br /&gt;
&lt;br /&gt;
2.3.4.5	 Detailed design report&lt;br /&gt;
A report should accompany the detailed designs, plans and estimates elaborating on the:&lt;br /&gt;
•	Engineering aspects,&lt;br /&gt;
•	Financial aspects,&lt;br /&gt;
•	Administrative aspects, &lt;br /&gt;
•	Tender documents &lt;br /&gt;
•	Specifications.&lt;br /&gt;
&lt;br /&gt;
2.3.4.6	 Project write-up to be submitted to potential financiers&lt;br /&gt;
Each Development Partner may have a different pattern of project presentation for financial request. The project document should therefore follow more guidelines as indicated by the financiers or the local funding sources where applicable.&lt;br /&gt;
&lt;br /&gt;
2.3.5	Project Phasing&lt;br /&gt;
Sometimes the implementation of a project is carried out in phases due to among other things, the following reasons:&lt;br /&gt;
•	Financial resources available,&lt;br /&gt;
•	Opportunity cost of money,&lt;br /&gt;
•	Economies of scale,&lt;br /&gt;
•	Growth rate in the area,&lt;br /&gt;
•	Rate of development in the area,&lt;br /&gt;
•	The design (working) life of various installations,&lt;br /&gt;
•	Development in levels of service,&lt;br /&gt;
•	New technology or method that needs piloting before rolling it out&lt;br /&gt;
Once the basic design period is decided (usually between 10 and 20 years) and water demand is computed for different years, the different elements can be phased. Exceptions do occur where financial assistance capital is being used and there is fear or a probability that further trunches will not be available just a few years later.&lt;br /&gt;
&lt;br /&gt;
Generally, phasing should be undertaken as follows: &lt;br /&gt;
(i)	Dams, river and spring intakes, should be implemented in a single phase to cover all of the ultimate design demand or the hydrologically calculated water availability. This is particularly significant for dams as flood spillways form an expensive integral part and the need to raise a spillway inlet and deal with the additional energy at its exit is usually very costly.&lt;br /&gt;
(ii)	Boreholes to be constructed in Multiple Phases according to the growth in demand.&lt;br /&gt;
(iii)	Treatment plants and storage tanks to be constructed stepwise or in phases, according to the projected growth in demand.&lt;br /&gt;
(iv)	Mechanical installations to be implemented in Multiple Phases according to the design life of the equipment.&lt;br /&gt;
(v)	Pump houses constructed in a Single Phase with space for additional mechanical plant.&lt;br /&gt;
(vi)	Rising mains and main conduits between units to be constructed to cover the ultimate demand in a single Phase.&lt;br /&gt;
(vii)	Long transmission mains to be constructed as two parallel lines in a single Phase where funds allow or in Two Phases where not. It can be advantageous to dedicate one of two parallel transmission mains to supplying water to the terminal reservoir whilst using the second for a mix of local distribution (daytime) and conveyance to the terminal reservoir (night time).&lt;br /&gt;
(viii)	Distribution systems to be constructed according to the growth in development in Multiple Phases.&lt;br /&gt;
&lt;br /&gt;
2.3.6	Procurement&lt;br /&gt;
2.3.6.1	2.2.6.1 Preparation of Tender Documents&lt;br /&gt;
The Procurement Management Unit (PMU) using the approved templates as guided by PPRA documentation undertakes preparation of tender documents. In preparing the tender documents undertaken by PMU, unit rate contract is normally adopted for project components such as intake, delivery mains, distribution system, storage tanks and other appurtenances. For specialized areas like the treatment plants and pumping stations it may be necessary to prepare separate tenders for the supply and installation of such facilities. The superstructure may still be included in the main contract bill of quantities. As much as possible one contract is preferred. The suppliers of such specialized equipment would then be included as sub-contractors of the main contractor. Important documents included in contract documents includes:&lt;br /&gt;
•	Letter of Invitation to Tender &lt;br /&gt;
•	Instruction to Tenderers &lt;br /&gt;
•	General Conditions of Contract&lt;br /&gt;
•	Special Conditions of Contract&lt;br /&gt;
•	Drawings &lt;br /&gt;
•	Specifications &lt;br /&gt;
•	Bills of Quantities&lt;br /&gt;
•	Tender Forms&lt;br /&gt;
•	Security Forms &lt;br /&gt;
•	Anti-bribery Pledge&lt;br /&gt;
•	Schedule of Additional Information&lt;br /&gt;
•	Information Data&lt;br /&gt;
&lt;br /&gt;
2.3.6.2	Tendering process&lt;br /&gt;
This process involves use of public procurement act to select service providers as detailed in following steps; &lt;br /&gt;
•	Issue of tender documents&lt;br /&gt;
•	Submission and receipt of tenders&lt;br /&gt;
•	Opening of tenders&lt;br /&gt;
•	Evaluation of tenders&lt;br /&gt;
•	Award of tender&lt;br /&gt;
•	Signing of contract agreement&lt;br /&gt;
&lt;br /&gt;
2.3.7	Implementation/Construction Stage&lt;br /&gt;
Construction stage includes contract management, Contract supervision and administration.&lt;br /&gt;
2.3.7.1	Contract Management&lt;br /&gt;
Contract management entails the following;&lt;br /&gt;
•	Contract Management Plan (CMP),&lt;br /&gt;
•	Contract Delivery Follow-up,&lt;br /&gt;
•	Work progress monitoring &amp;amp; control,  &lt;br /&gt;
•	All projects executed must have a completion report (as constructed built reports and drawings). It is essential that Engineers or Foremen keep an up to date record of all project activities including all changes to the original design with reasons for this clearly indicated as well as the approving authority.&lt;br /&gt;
•	Initial and Final Acceptance of the Works&lt;br /&gt;
•	Contract Close Out&lt;br /&gt;
2.3.7.2	Contract supervision and administration &lt;br /&gt;
During construction stage, it is necessary to consider the following;&lt;br /&gt;
•	Each phase of the project implementation should be planned in detail using techniques such as the Critical Path Method (CPM) or Programme Evaluation or/and Review Technique (PERT ) to ensure time control,&lt;br /&gt;
•	Work together with the Contractor to prepare a Quality Assurance Plan which shall narrate the scope of the works and the expected quality requirements for the project, the role of the participants in ensuring quality requirements are met&lt;br /&gt;
•	Obtain a cash flow forecast from the contractor, and make the Client aware of his payment obligations based on the forecast&lt;br /&gt;
•	Keep a close track of all contractors approved claims and adjust the contract price to reflect increase or decrease in the contract price&lt;br /&gt;
Detailed information in procurement, contract management, contract supervision and administration is detailed well in chapter three and four of Volume III Construction Supervision for Water Supply and Sanitation Projects.&lt;br /&gt;
&lt;br /&gt;
2.3.8	Operation and Maintenance Stage&lt;br /&gt;
   This process takes over after the project completion, it involves;&lt;br /&gt;
•	Preparation of O&amp;amp;M Plan,&lt;br /&gt;
•	Development of Individual Unit Plans for O&amp;amp;M,&lt;br /&gt;
•	Plan for capacity Building of O&amp;amp;M Personnel,&lt;br /&gt;
•	Plan for Providing Spares and Tools,&lt;br /&gt;
•	Plan for Water Audit and Leakage Control,&lt;br /&gt;
•	Plan for Efficient Use of Power,&lt;br /&gt;
•	Plan for sound financial management system,&lt;br /&gt;
•	Plan for Information Education Communication for Water and Sanitation Services,&lt;br /&gt;
•	Reports and Record Keeping,&lt;br /&gt;
•	Develop appropriate maintenance schedule and check lists,&lt;br /&gt;
•	Utilize Standard Operating Procedures,&lt;br /&gt;
•	Utilize Water Safety Plans.&lt;br /&gt;
&lt;br /&gt;
Detailed information on planning for operation and maintenance is found in chapter three and four of Volume IV Operation and Maintenance of Water Supply and Sanitation Projects&lt;br /&gt;
&lt;br /&gt;
2.3.9	Performance Monitoring&lt;br /&gt;
The aim of the project is to provide the services uninterrupted. To ensure this, a proper monitoring mechanism of the performance of the project should be prepared. Such a mechanism could include proper procedures for procurement and distribution of spare parts, fuel, replacement, a maintenance programme for the project including personnel at the village, District and if necessary at Regional and National levels also. Likewise a water quality surveillance procedure should be instituted in the framework of the existing mechanism.&lt;br /&gt;
&lt;br /&gt;
2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans&lt;br /&gt;
It is imperative that during planning of the water supply and sanitation project, designer should consult the Integrated Water Resources Management and Development (IWRMD) plan for a basin where the project is planned to be executed. The development of an IWRMD Plan is a key objective of the water resources component of the Water Sector Development Programme 2006-2025. It is a legal requirement provided for in the Water Resources Management Act, No. 11 of 2009. The plan provides a blueprint for sustainable development and management of the basin’s water resources. &lt;br /&gt;
&lt;br /&gt;
Thus, a water supply and sanitation project designer is advised and encouraged to consult IWRMD plans as they provide:&lt;br /&gt;
&lt;br /&gt;
•	The status of water resource availability (both quantity and quality) in the basin,&lt;br /&gt;
•	Water data and information necessary for the design of the projects,&lt;br /&gt;
•	Framework for water allocations among its competing demands,&lt;br /&gt;
•	Water demand for water related sectors,&lt;br /&gt;
•	Stakeholders consultation plan.&lt;br /&gt;
&lt;br /&gt;
2.4.1	Status of Development and Implementation of IWRMD Plans&lt;br /&gt;
By the time of development of this DCOM manual, IWRMD plans had been developed for six (6) out of the nine basins. The six basins are:&lt;br /&gt;
•	Rufiji River Basin,&lt;br /&gt;
•	Ruvuma and Southern Coast Basin,&lt;br /&gt;
•	Lake Tanganyika Basin,&lt;br /&gt;
•	Lake Nyasa Basin,&lt;br /&gt;
•	Internal Drainage and&lt;br /&gt;
•	Lake Rukwa Basin&lt;br /&gt;
&lt;br /&gt;
It was reported that the development of IWRMD plans for Lake Victoria Basin and Wami/Ruvu basins were on-going. &lt;br /&gt;
&lt;br /&gt;
IWRMD plans implementation challenges have been observed in some basins. These include:&lt;br /&gt;
&lt;br /&gt;
•	Inadequate funding to implement plans recommendations,&lt;br /&gt;
•	Some plans are not implementable because of including unrealistic recommendations,&lt;br /&gt;
•	Some plans are considered to have been more of studies rather than plans,&lt;br /&gt;
•	Inadequate human resources capacity to implement them,&lt;br /&gt;
•	As required by EMA, ESIAs have not been conducted, contrary to the requirement&lt;br /&gt;
&lt;br /&gt;
2.4.2	Components of IWRMD Plans&lt;br /&gt;
The developed IWRMD plans are expected to have the following main components:&lt;br /&gt;
&lt;br /&gt;
•	Component 1: Inventory and review of water availability, use and demand,&lt;br /&gt;
•	Component 2: Institutional, Policy and legal framework,&lt;br /&gt;
•	Component 3: Sector/Thematic Water Plans,&lt;br /&gt;
•	Component 4: Integrated Water Resources Management and Development Plan, &lt;br /&gt;
•	Component 5: IWRMD Plan Implementation Strategy and Action Plan.&lt;br /&gt;
&lt;br /&gt;
The production capacity of a source is very important in planning a water supply system. An estimate of the water that can be reliably produced by a water source like a well or spring gives the planner a basis to decide for or against its development. For the source(s) to be considered adequate, they must at least satisfy the maximum daily demand of the area to be served.&lt;br /&gt;
&lt;br /&gt;
2.5		Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change &lt;br /&gt;
&lt;br /&gt;
Water Safety Plan (WSP) is the most effective means of consistently ensuring the safety of a drinking-water supply through the use of a comprehensive risk assessment and risk management approach that encompasses all steps in water supply from the catchment to the consumer (WHO, 2017). The approach enables the operators and managers of water utilities to know the system thoroughly, identify where and how problems could arise, put multiple barriers and management systems in place to stop the problems before they happen and making all parts of the system work properly so as to ensure the safety and acceptability of a drinking water supply intended for human consumption and other domestic uses as summarized in the WHO safe water chain frameworks.&lt;br /&gt;
&lt;br /&gt;
Thus, during the planning phase, a designer should consult guidelines for the preparation of Water Safety Plans - Resilient to Climate Change, which has been prepared and published by Ministry of Water (MoW, 2015)&lt;br /&gt;
&lt;br /&gt;
2.6	Environmental and Social Impact Assessment Compliance&lt;br /&gt;
Section 81 of the Environmental Management Act (Cap 191) requires all developers of projects identified in the 3rd Schedule of the Act and detailed in the 1st Schedule of the Environmental Management (Environmental Impact Assessment And Audit) (Amendment) Regulations, 2018, to undertake Environmental Impact Assessment (EIA). Section 82 of EMA (Cap 181) requires that the EIA be carried out prior to the commencement or financing of the project. Procedures for carrying out the EIA, identified under the EIA and Audit  (Amendment) Regulations of 2018 identify eight steps to be followed. According to EIA and Audit (Amendment) Regulations of 2018, projects are classified into the following categories, namely:&lt;br /&gt;
&lt;br /&gt;
(a) “A” category for Mandatory projects;&lt;br /&gt;
 (b) “B1” category for Borderline Project;&lt;br /&gt;
(c) “B2” category for Non-Mandatory; and&lt;br /&gt;
(d) “Special Category&lt;br /&gt;
&lt;br /&gt;
So it is imperative that a proponent and developer of any water supply and sanitation project categorizes their project prior to actual project implementation for the same.&lt;br /&gt;
&lt;br /&gt;
2.6.1	Procedures for Conducting ESIA in Tanzania&lt;br /&gt;
Procedures for carrying out the ESIA, identified under the EIA and Audit (Amendment) Regulations of 2018 identify eight key steps to be followed in the EIA process in Tanzania. These are:&lt;br /&gt;
&lt;br /&gt;
•	Step 1: Registration,&lt;br /&gt;
•	Step 2: Screening, &lt;br /&gt;
•	Step 3: Scoping,&lt;br /&gt;
•	Step 4: Environmental Assessment,&lt;br /&gt;
•	Step 5: Review,&lt;br /&gt;
•	Step 6: Recommendations of the Technical Advisory Committee (TAC),&lt;br /&gt;
•	Step 7: Submission To The Minister For Environment,&lt;br /&gt;
•	Step 8: Approval of the EIS.&lt;br /&gt;
&lt;br /&gt;
It is recommended to consult NEMC guidelines and Environmental Management (Environmental Impact Assessment And Audit) (Amendment) Regulations, 2018 for more details. Also, the following Ministry of Water guidelines, accessible at have to be consulted.&lt;br /&gt;
a)	Guidelines of Good Environmental and Social Practices (GGESP) of July 2019,&lt;br /&gt;
b)	Environmental and Social Management Framework (ESMF) of July 2019.&lt;br /&gt;
&lt;br /&gt;
2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance&lt;br /&gt;
&lt;br /&gt;
Section 105 part (2) of the Environmental Act requires that wherever there is a major water project planned for construction, the Ministry responsible for water should conduct Strategic Environmental and Social Assessment. The strategic environmental assessment shall asses the area marked for development and include:&lt;br /&gt;
&lt;br /&gt;
•	Baseline environmental conditions and status of natural resources,&lt;br /&gt;
•	Identification of ecological sensitive and protected areas,&lt;br /&gt;
•	Identification and description of communities around the area,&lt;br /&gt;
•	Existing social-economic conditions,&lt;br /&gt;
•	Existing economic activities and infrastructure.&lt;br /&gt;
The strategic environmental and social assessment shall be submitted to the Minister responsible for Environment for approval before the planning process.&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
2.7	Potential Impacts of Climate Change on Water Supply Projects&lt;br /&gt;
It should be emphasized that immediately the project is conceived, hydrological, rainfall and other meteorological data collection must be initiated. In addition and given the long design life of such structures, consideration must be given to the possible impacts of climate change. Detailed account of predictions and impacts of climate change on water supply projects is provided in Appendix A.&lt;br /&gt;
&lt;br /&gt;
URT (2019) has recommended strategies and plans to adapt risks from climate change. The design related strategies of infrastructure, which a designer should consider while planning for water supply projects include:&lt;br /&gt;
&lt;br /&gt;
•	Where possible, have at least two sources of supply at different locations. Build superstructures above high flood-line level.&lt;br /&gt;
•	Adopt energy-efficiency programmes and, where possible, select facilities which require less power consumption.&lt;br /&gt;
•	Monitor wells near coastlines to prevent salinization. If climate change causes sea levels to rise dramatically, even aquifers that have been sustainably utilized can suffer salinization.&lt;br /&gt;
•	Utilize renewable energy sources.&lt;br /&gt;
&lt;br /&gt;
Guidelines for resiliency to climate change for urban water supply utilities have been published by the Ministry of Water. &lt;br /&gt;
&lt;br /&gt;
2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages&lt;br /&gt;
As explained in detail in section 2.1 of this volume, the CBWSOs have to  be involved in the complete life cycle of the project including ensuring their sustainability during operation and maintenance of the projects under the overall coordination of WSSAs and RUWASA.&lt;br /&gt;
&lt;br /&gt;
2.9	References&lt;br /&gt;
Asadieh, B. and Krakauer, N.Y. (2016). Impacts of changes in precipitation amount and distribution on water resources studied using a model rainwater harvesting system. J. Am. Water Resour. Assoc. 52: 1450–1471.https://doi.org/10.1111/ 1752-1688.12472.&lt;br /&gt;
&lt;br /&gt;
Gebrechorkos, S. H., Hülsmann, S., &amp;amp; Bernhofer, C. (2019). Regional climate projections for impact assessment studies in East Africa. Environmental Research Letters, 14(4), 044031. https://doi.org/10.1088/1748-9326/ab055a&lt;br /&gt;
&lt;br /&gt;
Giannini, A., M. Biasutti, I. Held, and A. Sobel (2008). A global perspective on African climate. Clim. Change, 90: 359–383.&lt;br /&gt;
&lt;br /&gt;
Hansingo, K., and C. Reason (2008). Modelling the atmospheric response to SST dipole patterns in the South Indian Ocean with a regional climate model. Meteorol. Atmos. Phys., 100: 37–52.&lt;br /&gt;
&lt;br /&gt;
Hansingo, K., and C. Reason (2009). Modelling the atmospheric response over southern Africa to SST forcing in the southeast tropical Atlantic and southwest subtropical Indian Oceans. Int. J. Climatol., 29: 1001–1012.&lt;br /&gt;
&lt;br /&gt;
Hermes, J., and C. Reason (2009). Variability in sea-surface temperature and winds in the tropical south-east Atlantic Ocean and regional rainfall relationships. Int. J. Climatol., 29: 11–21.&lt;br /&gt;
&lt;br /&gt;
IPCC (2007). Summary for policymakers Climate Change 2007: Impacts, Adaptation and Vulnerability. Contribution of Working Group II to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change ed M L Parry, O F Canziani, J P Palutikof, P J van der Linden and C E Hanson (Cambridge: Cambridge University Press) pp 7-22.&lt;br /&gt;
&lt;br /&gt;
IPCC (2014). Climate Change 2014: Summary for Policymakers, Synthesis Report. Contribution of Working Groups I, II and III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change [Core Writing Team, R.K. Pachauri and L.A. Meyer (eds.)]. IPCC, Geneva, Switzerland, 151 pp.&lt;br /&gt;
&lt;br /&gt;
Li, J., Chen, Y.D., Gan, T.Y., Lau, N. (2018). Elevated increases in human-perceived temperature under climate warming. Nat. Clim. Chang. 8: 43–47. https://doi.org/10.1038/s41558-017-0036-2.&lt;br /&gt;
&lt;br /&gt;
Marchant, R., C. Mumbi, S. Behera, and T. Yamagata (2007). The Indian Ocean dipole—the unsung driver of climatic variability in East Africa. Afr. J. Ecol., 45: 4–16.&lt;br /&gt;
&lt;br /&gt;
Moss, R. H. et al. (2010). The next generation of scenarios for climate change research and assessment. Nature, Vol 463, 11 February 2010, doi:10.1038/nature08823.&lt;br /&gt;
&lt;br /&gt;
Pohl, B., N. Fauchereau, C. Reason, and M. Rouault (2010). Relationships between the Antarctic Oscillation, the Madden - Julian Oscillation, and ENSO, and Consequences for Rainfall Analysis. J. Clim., 23: 238–254.&lt;br /&gt;
&lt;br /&gt;
Rouault, M., P. Florenchie, N. Fauchereau, and C. Reason (2003). South East tropical Atlantic warm events and southern African rainfall. Geophys. Res. Lett., 30, doi:10.1029/2002GL014840.&lt;br /&gt;
&lt;br /&gt;
UNFCCC (2010). The Cancun Agreements. United Nations Framework Convention on Climate Change http://unfccc.int/meetings/cancunnov2010/meeting/6266.php, 2010.&lt;br /&gt;
&lt;br /&gt;
URT (2019). Water sector development programme. Environmental and social management framework (ESMF). Revised version. Ministry of Water.&lt;br /&gt;
&lt;br /&gt;
Vautard, R., Gobiet, A., Sobolowski, S., Kjellström, E., Stegehuis, A., Watkiss, P., Mendlik. T., Landgren, O., Nikulin, G., Teichmann, C. and Jacob, D. (2014). The European climate under a 2°C global warming. Environ. Res. Letters. Environ. Res. Lett. 9, 034006, doi:10.1088/1748-9326/9/3/034006.&lt;br /&gt;
&lt;br /&gt;
Vigaud, N., Y. Richard, M. Rouault, and N. Fauchereau (2009). Moisture transport between the South Atlantic Ocean and southern Africa: Relationships with summer rainfall and associated dynamics. Clim. Dyn., 32: 113–123.&lt;br /&gt;
&lt;br /&gt;
WHO (2017). Climate-resilient water safety plans: Managing health risks associated with climate variability and change. World Health Organization. ISBN: 978-92-4-151279-4. Retrieved from: https://www.who.int/water_sanitation_health/publications/climate-resilient-water-safety-plans/en/&lt;br /&gt;
&lt;br /&gt;
Previous Page: [[Chapter One: Introduction|Chapter One: Introduction]] &amp;lt;&amp;lt;  &amp;gt;&amp;gt; Next Page: [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]]&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=Chapter_Two:_Project_Planning&amp;diff=512</id>
		<title>Chapter Two: Project Planning</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=Chapter_Two:_Project_Planning&amp;diff=512"/>
		<updated>2020-03-31T10:32:30Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;Arguably, planning of water supply projects is considered to be one of the most important stages in the design. Thus, it is strongly advised and emphasized that much time should be spent to undertake proper project planning. A proper project planning will ensure effective and efficient completion of the project successfully. In this chapter, project planning is presented in seven parts that are detailed below. These include:&lt;br /&gt;
&lt;br /&gt;
* Planning considerations for water supply projects&lt;br /&gt;
* Project Planning steps&lt;br /&gt;
* Consulting the Integrated Water Resources Management and Development Plan&lt;br /&gt;
* Consult guideline for preparation of Water Safety Plan – resilient to climate change.&lt;br /&gt;
* Environmental and Social Impact Assessment (ESIA) and Strategic Environmental and Social Impact Assessment (SESIA) Compliance&lt;br /&gt;
* Potential Impacts of Climate Change on Water Supply Projects&lt;br /&gt;
* Participation of CBWSOs in Project Planning Stages&lt;br /&gt;
&lt;br /&gt;
=Chapter Two: Project Planning=&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
2.1	Planning Considerations for Water Supply Projects &lt;br /&gt;
Before commencement of any development of a water project, it is essential to conduct project planning. Planning is a process that should entail the following:&lt;br /&gt;
•	Undertake ESIA and SESIA studies,&lt;br /&gt;
•	Engagement and involvement of the local community to instill the ownership, provide the local knowledge, project buy in and accommodate community needs and requirements,&lt;br /&gt;
•	Assess safe and reliable yield or discharge and quality of water source,&lt;br /&gt;
•	Determination of the system layout,&lt;br /&gt;
•	Conduct design of the water supply project,&lt;br /&gt;
•	Implement the project in terms of construction, operation and maintenance,&lt;br /&gt;
•	Work out to obtain a sound and robust project financing.&lt;br /&gt;
&lt;br /&gt;
It should be emphasized and stressed that collection of good quality, reliable, credible and enough data should be given high priority at all stages of project implementation. Population projection methods and their relevance for rural and urban settings or areas as recommended by the National Bureau of Statistics (NBS) have to be evaluated. Demographic features such as social and economic conditions have to be studied before design projections can be established. Also, water source reliability should be carried out before any further stage of project implementation.&lt;br /&gt;
2.2	Project Planning Steps&lt;br /&gt;
Project planning involves a series of steps that determine how project goals will be achieved. The goals may be solicited from the existing community or a strategic plan. In an event that there is not any plan, project plans can be developed through community meetings and gatherings, councils or board meetings, special focused group discussions or other planning processes. &lt;br /&gt;
&lt;br /&gt;
The main steps of project planning include:&lt;br /&gt;
Step 1: Initiation&lt;br /&gt;
Step 2: Pre-feasibility study&lt;br /&gt;
Step 3: Feasibility study&lt;br /&gt;
Step 4: Preliminary and Detailed Design&lt;br /&gt;
Step 5: Project phasing&lt;br /&gt;
Step 6: Procurement&lt;br /&gt;
Step 7: Implementation/Construction&lt;br /&gt;
Step 8: Operation and Maintenance (Management)&lt;br /&gt;
Step 9: Performance Monitoring&lt;br /&gt;
&lt;br /&gt;
The planning of water supply projects can be represented diagrammatically by a step wise planning cycle as shown in Figure 2.1.&lt;br /&gt;
&lt;br /&gt;
2.3	Pump Protection&lt;br /&gt;
The following sections provide a brief description of each of the twelve project planning steps.&lt;br /&gt;
&lt;br /&gt;
2.3.1	Initiation&lt;br /&gt;
Initiation or sometimes referred to as triggering stage, is a step where initial ideas of the project are presented. Community mobilization through awareness raising is conducted at this stage. The whole idea is to inform the community on the start of the project, solicit community input and knowledge about the project area. Project common understanding is also expected to be realized at this step. &lt;br /&gt;
&lt;br /&gt;
The outcome of this stage of planning is to acquire an understanding of the community conditions and identify problems that prevent the community from achieving its long-range goals. Community conditions which must be collected includes aspects of the community such as: &lt;br /&gt;
* Its geographic location, &lt;br /&gt;
* Demographics, &lt;br /&gt;
* Ecosystem, &lt;br /&gt;
* History,e.t.c&lt;br /&gt;
&lt;br /&gt;
The data collection for the above information should employ community assessment methods.&lt;br /&gt;
&lt;br /&gt;
[[File:Volume I Figure 2.1 Projects Planning Process.png|thumb|Figure 2.1: Projects Planning Process]]&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
Previous Page: [[Chapter One: Introduction|Chapter One: Introduction]] &amp;lt;&amp;lt;  &amp;gt;&amp;gt; Next Page: [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]]&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=Chapter_Two:_Project_Planning&amp;diff=511</id>
		<title>Chapter Two: Project Planning</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=Chapter_Two:_Project_Planning&amp;diff=511"/>
		<updated>2020-03-31T10:31:22Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;Arguably, planning of water supply projects is considered to be one of the most important stages in the design. Thus, it is strongly advised and emphasized that much time should be spent to undertake proper project planning. A proper project planning will ensure effective and efficient completion of the project successfully. In this chapter, project planning is presented in seven parts that are detailed below. These include:&lt;br /&gt;
&lt;br /&gt;
* Planning considerations for water supply projects&lt;br /&gt;
* Project Planning steps&lt;br /&gt;
* Consulting the Integrated Water Resources Management and Development Plan&lt;br /&gt;
* Consult guideline for preparation of Water Safety Plan – resilient to climate change.&lt;br /&gt;
* Environmental and Social Impact Assessment (ESIA) and Strategic Environmental and Social Impact Assessment (SESIA) Compliance&lt;br /&gt;
* Potential Impacts of Climate Change on Water Supply Projects&lt;br /&gt;
* Participation of CBWSOs in Project Planning Stages&lt;br /&gt;
&lt;br /&gt;
=Chapter Two: Project Planning=&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
2.1	Planning Considerations for Water Supply Projects &lt;br /&gt;
Before commencement of any development of a water project, it is essential to conduct project planning. Planning is a process that should entail the following:&lt;br /&gt;
•	Undertake ESIA and SESIA studies,&lt;br /&gt;
•	Engagement and involvement of the local community to instill the ownership, provide the local knowledge, project buy in and accommodate community needs and requirements,&lt;br /&gt;
•	Assess safe and reliable yield or discharge and quality of water source,&lt;br /&gt;
•	Determination of the system layout,&lt;br /&gt;
•	Conduct design of the water supply project,&lt;br /&gt;
•	Implement the project in terms of construction, operation and maintenance,&lt;br /&gt;
•	Work out to obtain a sound and robust project financing.&lt;br /&gt;
&lt;br /&gt;
It should be emphasized and stressed that collection of good quality, reliable, credible and enough data should be given high priority at all stages of project implementation. Population projection methods and their relevance for rural and urban settings or areas as recommended by the National Bureau of Statistics (NBS) have to be evaluated. Demographic features such as social and economic conditions have to be studied before design projections can be established. Also, water source reliability should be carried out before any further stage of project implementation.&lt;br /&gt;
2.2	Project Planning Steps&lt;br /&gt;
Project planning involves a series of steps that determine how project goals will be achieved. The goals may be solicited from the existing community or a strategic plan. In an event that there is not any plan, project plans can be developed through community meetings and gatherings, councils or board meetings, special focused group discussions or other planning processes. &lt;br /&gt;
&lt;br /&gt;
The main steps of project planning include:&lt;br /&gt;
Step 1: Initiation&lt;br /&gt;
Step 2: Pre-feasibility study&lt;br /&gt;
Step 3: Feasibility study&lt;br /&gt;
Step 4: Preliminary and Detailed Design&lt;br /&gt;
Step 5: Project phasing&lt;br /&gt;
Step 6: Procurement&lt;br /&gt;
Step 7: Implementation/Construction&lt;br /&gt;
Step 8: Operation and Maintenance (Management)&lt;br /&gt;
Step 9: Performance Monitoring&lt;br /&gt;
&lt;br /&gt;
The planning of water supply projects can be represented diagrammatically by a step wise planning cycle as shown in Figure 2.1.&lt;br /&gt;
&lt;br /&gt;
2.3	Pump Protection&lt;br /&gt;
The following sections provide a brief description of each of the twelve project planning steps.&lt;br /&gt;
&lt;br /&gt;
2.3.1	Initiation&lt;br /&gt;
Initiation or sometimes referred to as triggering stage, is a step where initial ideas of the project are presented. Community mobilization through awareness raising is conducted at this stage. The whole idea is to inform the community on the start of the project, solicit community input and knowledge about the project area. Project common understanding is also expected to be realized at this step. &lt;br /&gt;
&lt;br /&gt;
The outcome of this stage of planning is to acquire an understanding of the community conditions and identify problems that prevent the community from achieving its long-range goals. Community conditions which must be collected includes aspects of the community such as: &lt;br /&gt;
•	Its geographic location, &lt;br /&gt;
•	Demographics, &lt;br /&gt;
•	Ecosystem, &lt;br /&gt;
•	History,e.t.c&lt;br /&gt;
&lt;br /&gt;
The data collection for the above information should employ community assessment methods.&lt;br /&gt;
&lt;br /&gt;
[[File:Volume I Figure 2.1 Projects Planning Process.png|thumb|Figure 2.1: Projects Planning Process]]&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
Previous Page: [[Chapter One: Introduction|Chapter One: Introduction]] &amp;lt;&amp;lt;  &amp;gt;&amp;gt; Next Page: [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]]&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=File:Volume_I_Figure_2.1_Projects_Planning_Process.png&amp;diff=510</id>
		<title>File:Volume I Figure 2.1 Projects Planning Process.png</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=File:Volume_I_Figure_2.1_Projects_Planning_Process.png&amp;diff=510"/>
		<updated>2020-03-31T10:30:50Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;Figure 2.1: Projects Planning Process&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=509</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=509"/>
		<updated>2020-03-31T10:21:55Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Preface|Preface]] || i&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Acknowledgements|Acknowledgements]] || ii&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[List_of_Special_Committee_Members|List of Special Committee Members]] || iii&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[List_of_Abbreviations|List of Abbreviations]] || iv&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 15 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 16 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 17 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 18 || Apendices: Appendices&lt;br /&gt;
* [[DCOM Volume I Appendix A|Appendix A: Climate Change and Resilience to Climate Change	]]&lt;br /&gt;
* [[DCOM Volume I Appendix B|Appendix B: Minimum Water Flow Requirement for Fire Fighting	]]&lt;br /&gt;
* [[DCOM Volume I Appendix C|Appendix C: Example: Estimating The Capacity Of Tank	]]&lt;br /&gt;
* [[DCOM Volume I Appendix D|Appendix D: Structural Design of Concrete	]]&lt;br /&gt;
* [[DCOM Volume I Appendix E|Appendix E: Supply Pumping Systems	]]&lt;br /&gt;
* [[DCOM Volume I Appendix F|Appendix F: Source of Pumping Power	]]&lt;br /&gt;
* [[DCOM Volume I Appendix G|Appendix G: Additional Details of Various Unit Oprations	]]&lt;br /&gt;
* [[DCOM Volume I Appendix H|Appendix H: Methods for Disinfecting Water	]]&lt;br /&gt;
* [[DCOM Volume I Appendix I|Appendix I: Measurements of Water Hardness	]]&lt;br /&gt;
* [[DCOM Volume I Appendix J|Appendix J: Basic Statistics Used in Estimation of Design of Flood Events	]]&lt;br /&gt;
* [[DCOM Volume I Appendix K|Appendix K: Dams Detail Design	]]&lt;br /&gt;
* [[DCOM Volume I Appendix L|Appendix L: Standard Drawings	]]&lt;br /&gt;
* [[DCOM Volume I Appendix M|Appendix M: Selected Intake Designs	]]&lt;br /&gt;
|| 231&lt;br /&gt;
|}&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=508</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=508"/>
		<updated>2020-03-31T10:21:17Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Preface|Preface]] || i&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Acknowledgements|Acknowledgements]] || ii&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[List_of_Special_Committee_Members|List of Special Committee Members]] || iii&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[List_of_Abbreviations|List of Abbreviations]] || iv&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 15 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 16 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 17 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 18 || [[Apendices: Appendices]] &lt;br /&gt;
* [[DCOM Volume I Appendix A|Appendix A: Climate Change and Resilience to Climate Change	]]&lt;br /&gt;
* [[DCOM Volume I Appendix B|Appendix B: Minimum Water Flow Requirement for Fire Fighting	]]&lt;br /&gt;
* [[DCOM Volume I Appendix C|Appendix C: Example: Estimating The Capacity Of Tank	]]&lt;br /&gt;
* [[DCOM Volume I Appendix D|Appendix D: Structural Design of Concrete	]]&lt;br /&gt;
* [[DCOM Volume I Appendix E|Appendix E: Supply Pumping Systems	]]&lt;br /&gt;
* [[DCOM Volume I Appendix F|Appendix F: Source of Pumping Power	]]&lt;br /&gt;
* [[DCOM Volume I Appendix G|Appendix G: Additional Details of Various Unit Oprations	]]&lt;br /&gt;
* [[DCOM Volume I Appendix H|Appendix H: Methods for Disinfecting Water	]]&lt;br /&gt;
* [[DCOM Volume I Appendix I|Appendix I: Measurements of Water Hardness	]]&lt;br /&gt;
* [[DCOM Volume I Appendix J|Appendix J: Basic Statistics Used in Estimation of Design of Flood Events	]]&lt;br /&gt;
* [[DCOM Volume I Appendix K|Appendix K: Dams Detail Design	]]&lt;br /&gt;
* [[DCOM Volume I Appendix L|Appendix L: Standard Drawings	]]&lt;br /&gt;
* [[DCOM Volume I Appendix M|Appendix M: Selected Intake Designs	]]&lt;br /&gt;
|| 231&lt;br /&gt;
|-&lt;br /&gt;
| || &lt;br /&gt;
&lt;br /&gt;
 || &lt;br /&gt;
|}&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=Main_Page&amp;diff=507</id>
		<title>Main Page</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=Main_Page&amp;diff=507"/>
		<updated>2020-03-31T10:18:48Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;The four volumes of the DCOM manual have been prepared in order to facilitate effective complimentary planning, design, construction supervision as well as operation and maintenance of water supply and sanitation projects for urban, peri-urban and rural areas of Tanzania. The manuals will also assist the staff of the Ministry responsible for Water to undertake their supervisory and coordination roles well and the consultants to undertake designs using the guidelines recommended in the MoW manual. Furthermore, the '''''[[Appendix_M:_Standard_Drawings|Engineering Drawings]]''''' are attached as [http://design.maji.go.tz/index.php/Appendix_M:_Standard_Drawings Volume I Appendix M]&lt;br /&gt;
__NOTOC__ &lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot; style=&amp;quot;float: left; border: 0px solid #BBB; margin: .46em 0 0 .2em;&amp;quot;&lt;br /&gt;
|- style=&amp;quot;font-size: 86%;&amp;quot;&lt;br /&gt;
|valign=&amp;quot;top&amp;quot; |&lt;br /&gt;
&lt;br /&gt;
[[Image:DCOM_Volume_I_2020-03-11.png|340px|link=DCOM_Volume_I]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]] or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
|valign=&amp;quot;top&amp;quot; |&lt;br /&gt;
[[Image:DCOM_Volume_II_2020-03-11.png|340px|link=Volume II: Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume II: Design of Sanitation Projects &amp;lt;/h4&amp;gt;[[Volume II: Preface|Readmore...]] or Download  [[:File:DCOM_VOLUME_II_2020-03-11.pdf| Volume II PDF]]&lt;br /&gt;
|-&lt;br /&gt;
|valign=&amp;quot;top&amp;quot; |&lt;br /&gt;
[[Image:DCOM_Volume_III_2020-03-11.png|340px|link=Volume III: Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume III: Construction Supervision for&amp;lt;br /&amp;gt;&lt;br /&gt;
Water Supply and Sanitation Projects &amp;lt;br /&amp;gt; &amp;lt;/h4&amp;gt;[[Volume III: Preface|Readmore...]] or Download  [[:File:DCOM_VOLUME_III_2020-03-11.pdf| Volume III PDF]]&lt;br /&gt;
&lt;br /&gt;
|valign=&amp;quot;top&amp;quot; |&lt;br /&gt;
[[Image:DCOM_Volume_IV_2020-03-11.png|340px|link=Volume IV: Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume IV: Operation and Maintenance &amp;lt;br /&amp;gt; of Water&lt;br /&gt;
Supply and Sanitation Projects &amp;lt;br /&amp;gt; &amp;lt;/h4&amp;gt;[[Volume IV: Preface|Readmore...]]or Download  [[:File:DCOM_Volume_IV_2020-03-11.pdf| Volume IV PDF]]&lt;br /&gt;
&lt;br /&gt;
|}&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=506</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=506"/>
		<updated>2020-03-31T10:15:43Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Preface|Preface]] || i&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Acknowledgements|Acknowledgements]] || ii&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[List_of_Special_Committee_Members|List of Special Committee Members]] || iii&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[List_of_Abbreviations|List of Abbreviations]] || iv&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 15 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 16 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 17 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 18 || [[Apendices: Appendices]] || 231&lt;br /&gt;
|-&lt;br /&gt;
| || &lt;br /&gt;
* [[DCOM Volume I Appendix A|Appendix A: Climate Change and Resilience to Climate Change	]]&lt;br /&gt;
* [[DCOM Volume I Appendix B|Appendix B: Minimum Water Flow Requirement for Fire Fighting	]]&lt;br /&gt;
* [[DCOM Volume I Appendix C|Appendix C: Example: Estimating The Capacity Of Tank	]]&lt;br /&gt;
* [[DCOM Volume I Appendix D|Appendix D: Structural Design of Concrete	]]&lt;br /&gt;
* [[DCOM Volume I Appendix E|Appendix E: Supply Pumping Systems	]]&lt;br /&gt;
* [[DCOM Volume I Appendix F|Appendix F: Source of Pumping Power	]]&lt;br /&gt;
* [[DCOM Volume I Appendix G|Appendix G: Additional Details of Various Unit Oprations	]]&lt;br /&gt;
* [[DCOM Volume I Appendix H|Appendix H: Methods for Disinfecting Water	]]&lt;br /&gt;
* [[DCOM Volume I Appendix I|Appendix I: Measurements of Water Hardness	]]&lt;br /&gt;
* [[DCOM Volume I Appendix J|Appendix J: Basic Statistics Used in Estimation of Design of Flood Events	]]&lt;br /&gt;
* [[DCOM Volume I Appendix K|Appendix K: Dams Detail Design	]]&lt;br /&gt;
* [[DCOM Volume I Appendix L|Appendix L: Standard Drawings	]]&lt;br /&gt;
* [[DCOM Volume I Appendix M|Appendix M: Selected Intake Designs	]]&lt;br /&gt;
 || &lt;br /&gt;
|}&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=505</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=505"/>
		<updated>2020-03-31T10:13:04Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Preface|Preface]] || i&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Acknowledgements|Acknowledgements]] || ii&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[List_of_Special_Committee_Members|List of Special Committee Members]] || iii&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[List_of_Abbreviations|List of Abbreviations]] || iv&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 15 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 16 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 17 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 18 || [[Apendices: Appendices]] || 231&lt;br /&gt;
|-&lt;br /&gt;
| || &lt;br /&gt;
* [[v1appendixA|Appendix A: Climate Change and Resilience to Climate Change	]]&lt;br /&gt;
* Appendix B: Minimum Water Flow Requirement for Fire Fighting	&lt;br /&gt;
* Appendix C: Example: Estimating The Capacity Of Tank	&lt;br /&gt;
* Appendix D: Structural Design of Concrete	&lt;br /&gt;
* Appendix E: Supply Pumping Systems	&lt;br /&gt;
* Appendix F: Source of Pumping Power	&lt;br /&gt;
* Appendix G: Additional Details of Various Unit Oprations	&lt;br /&gt;
* Appendix H: Methods for Disinfecting Water	&lt;br /&gt;
* Appendix I: Measurements of Water Hardness	&lt;br /&gt;
* Appendix J: Basic Statistics Used in Estimation of Design of Flood Events	&lt;br /&gt;
* Appendix K: Dams Detail Design	&lt;br /&gt;
* Appendix L: Standard Drawings	&lt;br /&gt;
* Appendix M: Selected Intake Designs	&lt;br /&gt;
 || &lt;br /&gt;
|}&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=504</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=504"/>
		<updated>2020-03-31T10:11:10Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Preface|Preface]] || i&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Acknowledgements|Acknowledgements]] || ii&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[List_of_Special_Committee_Members|List of Special Committee Members]] || iii&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[List_of_Abbreviations|List of Abbreviations]] || iv&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 15 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 16 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 17 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 18 || [[Apendices: Appendices]] || 231&lt;br /&gt;
|-&lt;br /&gt;
| || &lt;br /&gt;
* Appendix A: Climate Change and Resilience to Climate Change	&lt;br /&gt;
* Appendix B: Minimum Water Flow Requirement for Fire Fighting	&lt;br /&gt;
* Appendix C: Example: Estimating The Capacity Of Tank	&lt;br /&gt;
* Appendix D: Structural Design of Concrete	&lt;br /&gt;
* Appendix E: Supply Pumping Systems	&lt;br /&gt;
* Appendix F: Source of Pumping Power	&lt;br /&gt;
* Appendix G: Additional Details of Various Unit Oprations	&lt;br /&gt;
* Appendix H: Methods for Disinfecting Water	&lt;br /&gt;
* Appendix I: Measurements of Water Hardness	&lt;br /&gt;
* Appendix J: Basic Statistics Used in Estimation of Design of Flood Events	&lt;br /&gt;
* Appendix K: Dams Detail Design	&lt;br /&gt;
* Appendix L: Standard Drawings	&lt;br /&gt;
* Appendix M: Selected Intake Designs	&lt;br /&gt;
 || &lt;br /&gt;
|}&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=503</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=503"/>
		<updated>2020-03-31T10:07:50Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Preface|Preface]] || i&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Acknowledgements|Acknowledgements]] || ii&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[List_of_Special_Committee_Members|List of Special Committee Members]] || iii&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[List_of_Abbreviations|List of Abbreviations]] || iv&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 15 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 16 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 17 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 18 || [[Apendices: Appendices]] || 231&lt;br /&gt;
|-&lt;br /&gt;
| 18 || &lt;br /&gt;
* APPENDIX A: CLIMATE CHANGE AND RESILIENCE TO CLIMATE CHANGE	232&lt;br /&gt;
* APPENDIX B: MINIMUM WATER FLOW REQUIREMENT FOR FIRE FIGHTING	237&lt;br /&gt;
* APPENDIX C: EXAMPLE: ESTIMATING THE CAPACITY OF TANK	239&lt;br /&gt;
* APPENDIX D: STRUCTURAL DESIGN OF CONCRETE	241&lt;br /&gt;
* APPENDIX E: SUPPLY PUMPING SYSTEMS	251&lt;br /&gt;
* APPENDIX F: SOURCE OF PUMPING POWER	263&lt;br /&gt;
* APPENDIX G: ADDITIONAL DETAILS OF VARIOUS UNIT OPRATIONS	275&lt;br /&gt;
* APPENDIX H: METHODS FOR DISINFECTING WATER	281&lt;br /&gt;
* APPENDIX I: MEASUREMENTS OF WATER HARDNESS	287&lt;br /&gt;
* APPENDIX J: BASIC STATISTICS USED IN ESTIMATION OF DESIGN OF FLOOD EVENTS	289&lt;br /&gt;
* APPENDIX K: DAMS DETAIL DESIGN	294&lt;br /&gt;
* APPENDIX L: STANDARD DRAWINGS	306&lt;br /&gt;
* APPENDIX M: SELECTED INTAKE DESIGNS.	307&lt;br /&gt;
 || 231&lt;br /&gt;
|}&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=502</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=502"/>
		<updated>2020-03-31T09:51:52Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Preface|Preface]] || i&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Acknowledgements|Acknowledgements]] || ii&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[List_of_Special_Committee_Members|List of Special Committee Members]] || iii&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[List_of_Abbreviations|List of Abbreviations]] || iv&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 15 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 16 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 17 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 18 || [[Apendices: Appendices]] || 231&lt;br /&gt;
|}&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=501</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=501"/>
		<updated>2020-03-31T09:50:25Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Preface|Preface]] || i&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Acknowledgements|Acknowledgements]] || ii&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[List_of_Special_Committee_Members|List of Special Committee Members]] || iii&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[List_of_Abbreviations|List of Abbreviations]] || iv&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[List_of_Abbreviations|List of Abbreviations]] || iv&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 15 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 16 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 17 || [[Apendices: Appendices]] || 231&lt;br /&gt;
|}&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=500</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=500"/>
		<updated>2020-03-31T09:49:25Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Preface|Preface]] || i&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Acknowledgements|Acknowledgements]] || ii&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[List_of_Special_Committee_Members|List of Special Committee Members]] || iii&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[List_of_Abbreviations|List of Abbreviations]] || iv&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 15 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 16 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 17 || [[Apendices: Appendices]] || 231&lt;br /&gt;
|}&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=499</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=499"/>
		<updated>2020-03-31T08:39:20Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Preface|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Apendices: Appendices]] || 231&lt;br /&gt;
|}&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=498</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=498"/>
		<updated>2020-03-30T19:19:08Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Apendices: Appendices]] || 231&lt;br /&gt;
|}&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=497</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=497"/>
		<updated>2020-03-30T19:16:26Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Apendices: Appendices]] || 231&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Chapter_One:_Introduction|CHAPTER ONE: INTRODUCTION]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[CHAPTER TWO: PROJECT PLANNING|CHAPTER TWO: PROJECT PLANNING]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[CHAPTER THREE: WATER SOURCES ANALYSIS|CHAPTER THREE: WATER SOURCES ANALYSIS]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[CHAPTER FOUR: WATER DEMAND ASSESSMENT|CHAPTER FOUR: WATER DEMAND ASSESSMENT]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[CHAPTER FIVE: PIPELINES DESIGN|CHAPTER FIVE: PIPELINES DESIGN]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[CHAPTER SIX: PUMPING SYSTEMS|CHAPTER SIX: PUMPING SYSTEMS]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[CHAPTER SEVEN: WATER TREATMENT|CHAPTER SEVEN: WATER TREATMENT]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[CHAPTER EIGHT: TREATMENT OF WATERS WITH SPECIAL CONTAMINANTS|CHAPTER EIGHT: TREATMENT OF WATERS WITH SPECIAL CONTAMINANTS]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[CHAPTER NINE: DESIGN OF WATER STRUCTURES|CHAPTER NINE: DESIGN OF WATER STRUCTURES]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[CHAPTER TEN: APPLICATION SOFTWARE|CHAPTER TEN: APPLICATION SOFTWARE]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[CHAPTER ELEVEN: METERING|CHAPTER ELEVEN: METERING]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[CHAPTER TWELVE: DESIGN STANDARDS AND SPECIFICATIONS|CHAPTER TWELVE: DESIGN STANDARDS AND SPECIFICATIONS]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[CHAPTER THIRTEEN: ROLE OF STAKEHOLDERS IN DESIGN OF WATER SUPPLY PROJECTS|CHAPTER THIRTEEN: ROLE OF STAKEHOLDERS IN DESIGN OF WATER SUPPLY PROJECTS]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[APENDICES: APPENDICES]] || 231&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| Class=&amp;quot;Wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Apendices: Appendices]] || 231&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Chapter #!! Chapter Title!! Page&lt;br /&gt;
|-&lt;br /&gt;
| i || LIST OF SPECIAL COMMITTEE MEMBERS || V&lt;br /&gt;
|-&lt;br /&gt;
| 1|| CHAPTER ONE: INTRODUCTION		 || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1|| Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.1 || Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.2 || Climate Change and Resilience to Climate Change || 2&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.3 || Public-Private Partnership in Water Supply and Sanitation Projects in Developing Countries || 3&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.4 || International Water Law || 4&lt;br /&gt;
|-&lt;br /&gt;
| 1.2 || Development Agenda and Water and Sanitation Sector in Tanzania || 5&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.1 || National Water Policy || 7&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.2|| Legal and Institutional Framework for Water Supply and Sanitation Services || 8&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.3 || Coverage and Access to Water Supply Services || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.4|| Policy Environment for Water and Sanitation Services in Tanzania || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.5 || Major Stakeholders in  Water Supply and Sanitation Projects || 10&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.6 || Water Supply and Sanitation Public Private Partnership in Tanzania || 11&lt;br /&gt;
|-&lt;br /&gt;
| 1.3 || Rationale for Preparation of the Fourth Edition DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.4 || About the Fourth Edition of the DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.5 || Organisation of the 4th edition of the DCOM Manual || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.6 || Purpose of this Volume || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.7 || References	 || 15&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
* CHAPTER TWO	17&lt;br /&gt;
* PROJECT PLANNING	17&lt;br /&gt;
* 2.1	Planning Considerations for Water Supply Projects	17&lt;br /&gt;
* 2.2	Project Planning Steps	18&lt;br /&gt;
* 2.3	Pump Protection	18&lt;br /&gt;
* 2.3.1	Initiation	18&lt;br /&gt;
* 2.3.1.1	Community Assessment Steps	20&lt;br /&gt;
* 2.3.1.2	Methods of conducting community assessment	20&lt;br /&gt;
* 2.3.1.2.1	Comprehensive community assessment	20&lt;br /&gt;
* 2.3.1.2.2	Strategic community assessment	20&lt;br /&gt;
* 2.3.2	Pre-feasibility Study	21&lt;br /&gt;
* 2.3.3	Feasibility Study	21&lt;br /&gt;
* 2.3.3.1	Water Supply Projects Ranking and Technology Selection Criteria	22&lt;br /&gt;
* 2.3.3.1.1	Ranking of Projects	22&lt;br /&gt;
* 2.3.3.1.2	Choice of Technology	23&lt;br /&gt;
* 2.3.4	Preliminary and Detailed Design	23&lt;br /&gt;
* 2.3.4.1	Detailed Engineering Drawings	24&lt;br /&gt;
* 2.3.4.2	Detailed estimates of capital costs	24&lt;br /&gt;
* 2.3.4.3	Detailed estimates of recurrent costs	24&lt;br /&gt;
* 2.3.4.4	Anticipated revenue	25&lt;br /&gt;
* 2.3.4.5	Detailed design report	25&lt;br /&gt;
* 2.3.4.6	Project write-up to be submitted to potential financiers	25&lt;br /&gt;
* 2.3.5	Project Phasing	25&lt;br /&gt;
* 2.3.6	Procurement	26&lt;br /&gt;
* 2.3.6.1	2.2.6.1 Preparation of Tender Documents	26&lt;br /&gt;
* 2.3.6.2	Tendering process	27&lt;br /&gt;
* 2.3.7	Implementation/Construction Stage	27&lt;br /&gt;
* 2.3.7.1	Contract Management	27&lt;br /&gt;
* 2.3.7.2	Contract supervision and administration	27&lt;br /&gt;
* 2.3.8	Operation and Maintenance Stage	28&lt;br /&gt;
* 2.3.9	Performance Monitoring	28&lt;br /&gt;
* 2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans	28&lt;br /&gt;
* 2.4.1	Status of Development and Implementation of IWRMD Plans	29&lt;br /&gt;
* 2.4.2	Components of IWRMD Plans	30&lt;br /&gt;
* 2.5	Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change	30&lt;br /&gt;
* 2.6	Environmental and Social Impact Assessment Compliance	30&lt;br /&gt;
* 2.6.1	Procedures for Conducting ESIA in Tanzania	31&lt;br /&gt;
* 2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance	31&lt;br /&gt;
* 2.7	Potential Impacts of Climate Change on Water Supply Projects	32&lt;br /&gt;
* 2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages	32&lt;br /&gt;
* 2.9	References	32&lt;br /&gt;
* CHAPTER THREE	35&lt;br /&gt;
* WATER SOURCES ANALYSIS	35&lt;br /&gt;
* 3.1	Availability of Water Resources in Tanzania Mainland	35&lt;br /&gt;
* 3.2	Water Sources Available in Tanzania Mainland	38&lt;br /&gt;
* 3.2.1	Rainwater and fog harvesting	39&lt;br /&gt;
* 3.2.2	Surface Water	39&lt;br /&gt;
* 3.2.2.1	Rivers or streams	39&lt;br /&gt;
* 3.2.2.2	Impoundments	39&lt;br /&gt;
* 3.2.2.3	Springs	39&lt;br /&gt;
* 3.2.2.4	Lakes	39&lt;br /&gt;
* 3.2.2.5	Dams	40&lt;br /&gt;
* 3.2.3	Groundwater	40&lt;br /&gt;
* 3.2.3.1	Infiltration galleries/wells	40&lt;br /&gt;
* 3.2.3.2	Well	40&lt;br /&gt;
* 3.2.3.3	Classification of wells based on the aquifer tapped	41&lt;br /&gt;
* 3.2.3.3.1	Shallow wells	41&lt;br /&gt;
* 3.2.3.3.2	Deep wells	41&lt;br /&gt;
* 3.2.3.3.3	Artesian wells	41&lt;br /&gt;
* 3.3	Quality Suitability of Water Sources for Water Supply Projects	42&lt;br /&gt;
* 3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment	42&lt;br /&gt;
* 3.5	General Considerations for Selection of Water Sources	42&lt;br /&gt;
* 3.5.1	Adequacy and reliability	42&lt;br /&gt;
* 3.5.2	Quality of water sources	43&lt;br /&gt;
* 3.5.3	Technical Requirements	43&lt;br /&gt;
* 3.5.4	Cost implications to develop a water source	43&lt;br /&gt;
* 3.5.5	Protection of water sources	43&lt;br /&gt;
* 3.5.6	Legal and management requirements	44&lt;br /&gt;
* 3.5.7	Distance of water supply source	44&lt;br /&gt;
* 3.5.8	Topography of the project area and its surroundings	44&lt;br /&gt;
* 3.5.9	Elevation of a source of water supply	44&lt;br /&gt;
* 3.6	Determination of water source yield	44&lt;br /&gt;
* 3.6.1	Rainwater and fog harvesting	45&lt;br /&gt;
* 3.6.1.1	Rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.1	Types of rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.2	Components of rainwater harvesting system	46&lt;br /&gt;
* 3.6.1.1.3	Estimation of the yield	47&lt;br /&gt;
* 3.6.2	Hydrological Analysis of Surface Waters	47&lt;br /&gt;
* 3.7	Other considerations for various water sources	55&lt;br /&gt;
* 3.7.1	Water permits Considerations	55&lt;br /&gt;
* 3.7.2	Conservation of water sources	55&lt;br /&gt;
* 3.8	References	55&lt;br /&gt;
* CHAPTER FOUR	56&lt;br /&gt;
* WATER DEMAND ASSESSMENT	56&lt;br /&gt;
* 4.1	Water Demand Assessment	56&lt;br /&gt;
* 4.2	General Factors Affecting Water Demand Assessment	57&lt;br /&gt;
* 4.3	Determination of Water Demand for Different Uses	58&lt;br /&gt;
* Step 7. Establish Net Water Demand	67&lt;br /&gt;
* Step 9: Establish Operational water consumption	67&lt;br /&gt;
* Step 10: Establish System water losses	68&lt;br /&gt;
* Step 11 Establish Non-Revenue Water	69&lt;br /&gt;
* 4.4	Variations in Water Consumption	70&lt;br /&gt;
* 4.4.1	Definitions	70&lt;br /&gt;
* 4.4.2	Variation in the Rate of Consumption	71&lt;br /&gt;
* 4.4.2.1	Diurnal variation in demand	71&lt;br /&gt;
* 4.4.3	Peak Factors	72&lt;br /&gt;
* 4.4.4	Predicting Demand	74&lt;br /&gt;
* 4.4.5	Design Demand	75&lt;br /&gt;
* 4.5	References	75&lt;br /&gt;
* CHAPTER FIVE	76&lt;br /&gt;
* PIPELINES DESIGN	76&lt;br /&gt;
* 5.1	Design Requirements of pipelines	76&lt;br /&gt;
* 5.2	Types of pipelines	76&lt;br /&gt;
* 5.3	Security considerations for pipelines	76&lt;br /&gt;
* 5.3.1	Methods of water transmission and distribution	76&lt;br /&gt;
* 5.3.2	Gravity flow	77&lt;br /&gt;
* 5.3.3	Pumping with storage	77&lt;br /&gt;
* 5.3.4	Direct pumping to the distribution system	77&lt;br /&gt;
* 5.4	Pipeline Hydraulics Assessment	77&lt;br /&gt;
* 5.4.1	Pressure	77&lt;br /&gt;
* 5.4.2	Determination of Head Losses	77&lt;br /&gt;
* 5.5	Water supply transmission system	79&lt;br /&gt;
* 5.5.1	Determination of Transmission Pipe Size	79&lt;br /&gt;
* 5.5.2	Maximum Pressure	79&lt;br /&gt;
* 5.6	Distribution system	80&lt;br /&gt;
* 5.6.1	Branched System	80&lt;br /&gt;
* 5.6.2	Looped System	81&lt;br /&gt;
* 5.7	Pipe network analysis	82&lt;br /&gt;
* 5.7.1	Network analysis by Conventional method (Hardy Cross)	82&lt;br /&gt;
* 5.7.2	Network Analysis by Computer Software	82&lt;br /&gt;
* 5.7.2.1	EPANET Software	82&lt;br /&gt;
* 5.7.3	Pipeline design criteria	85&lt;br /&gt;
* 5.8	Pipeline materials selection	86&lt;br /&gt;
* 5.8.1	Considerations in Selecting Pipeline Materials	86&lt;br /&gt;
* 5.8.1.1	Flow Characteristics	86&lt;br /&gt;
* 5.8.1.2	Pipe Strength	86&lt;br /&gt;
* 5.8.1.3	Durability	87&lt;br /&gt;
* 5.8.1.4	Type of Soil	87&lt;br /&gt;
* 5.8.1.5	Availability	87&lt;br /&gt;
* 5.8.1.6	Cost of Pipes	87&lt;br /&gt;
* 5.8.2	Types of Pipe Materials Available	87&lt;br /&gt;
* 5.8.2.1	Galvanized Iron (GI) Pipes	87&lt;br /&gt;
* 5.8.2.2	Plastic Pipes	87&lt;br /&gt;
* 5.9	Appurtenances for transmission and distribution mains	88&lt;br /&gt;
* 5.9.1	Valves	89&lt;br /&gt;
* 5.9.1.1	Isolation Valves	89&lt;br /&gt;
* 5.9.1.2	Check Valves	89&lt;br /&gt;
* 5.9.1.3	Float Valves	89&lt;br /&gt;
* 5.9.1.4	Air Release Valves	89&lt;br /&gt;
* 5.9.1.5	Pressure Reducing Valves	89&lt;br /&gt;
* 5.9.1.6	Washout valves	89&lt;br /&gt;
* 5.9.2	Fittings	89&lt;br /&gt;
* 5.10	References	90&lt;br /&gt;
* CHAPTER SIX	91&lt;br /&gt;
* PUMPING SYSTEMS	91&lt;br /&gt;
* 6.1	Introduction	91&lt;br /&gt;
* 6.2	Rationale	91&lt;br /&gt;
* 6.3	Common Types of Pumps used in water supply	91&lt;br /&gt;
* 6.4	Pumping System Setup	91&lt;br /&gt;
* 6.5	Source of Pumping Power	92&lt;br /&gt;
* 6.6	Pumping system design pump selection	92&lt;br /&gt;
* 6.7	Pump Protection	95&lt;br /&gt;
* 6.8	References	95&lt;br /&gt;
* CHAPTER SEVEN	96&lt;br /&gt;
* WATER TREATMENT	96&lt;br /&gt;
* 7.1	Introduction	96&lt;br /&gt;
* 7.1.1	Classification of the qualities of water sources found in Tanzania according to the complexity of its treatment	96&lt;br /&gt;
* 7.1.2	Classification of Unit Operations to achieve water treatment levels	99&lt;br /&gt;
* 7.2	Recommended overall design approach for treatment plant components	99&lt;br /&gt;
* 7.3	Documents and websites consulted and those which are hyper-linked to the DCOM Manual	100&lt;br /&gt;
* 7.4	Water treatment design considerations	100&lt;br /&gt;
* 7.5	Water treatment levels and units	101&lt;br /&gt;
* 7.5.1	Pre-treatment	101&lt;br /&gt;
* 7.5.1.1	Scum and Floating Materials Skimmer	101&lt;br /&gt;
* 7.5.1.2	Screening or straining	101&lt;br /&gt;
* 7.5.1.3	Grit Removal	103&lt;br /&gt;
* 7.5.1.3.1	Design criteria	103&lt;br /&gt;
* 7.5.1.4	Sand Traps	105&lt;br /&gt;
* 7.5.1.5	Pre-chlorination	107&lt;br /&gt;
* 7.5.1.6	Water pre-conditioning (pH adjustment)	108&lt;br /&gt;
* 7.5.2	Primary Treatment	108&lt;br /&gt;
* 7.5.2.1	Sedimentation	108&lt;br /&gt;
* 7.5.2.2	Primary Filtration	114&lt;br /&gt;
* 7.5.2.2.1	Slow Sand Filtration	114&lt;br /&gt;
* 7.5.2.2.2	Rapid Gravity Sand Filtration	117&lt;br /&gt;
* 7.5.2.2.3	Comparison between Slow Sand Filters and Rapid Sand Filters	118&lt;br /&gt;
* 7.5.2.2.4	Other Types of Filters	119&lt;br /&gt;
* 7.5.2.3	Floatation	124&lt;br /&gt;
* 7.5.2.3.1	Dissolved-Air Floatation	124&lt;br /&gt;
* 7.5.2.3.2	Electrolytic Floatation	125&lt;br /&gt;
* 7.5.2.3.3	Dispersed-Air Floatation	125&lt;br /&gt;
* 7.5.2.4	Aeration	125&lt;br /&gt;
* 7.5.2.4.1	Falling Water Aerators	126&lt;br /&gt;
* 7.5.2.4.2	Spray Aerators	127&lt;br /&gt;
* 7.5.3	Secondary Treatment	130&lt;br /&gt;
* 7.5.3.1	Clarification	130&lt;br /&gt;
* 7.5.3.2	Coagulation	130&lt;br /&gt;
* 7.5.3.3	Flocculation	131&lt;br /&gt;
* 7.5.3.4	Filtration	131&lt;br /&gt;
* 7.5.4	Tertiary Treatment	132&lt;br /&gt;
* 7.5.4.1	Disinfection	132&lt;br /&gt;
* 7.5.4.1.1	Disinfection Methods	132&lt;br /&gt;
* 7.5.4.1.2	Chlorinators	132&lt;br /&gt;
* 7.5.4.1.3	Design considerations for chlorinators	133&lt;br /&gt;
* 7.5.4.2	Ozonation	133&lt;br /&gt;
* 7.5.4.3	Water softening	134&lt;br /&gt;
* 7.5.4.3.1	Methods of Softening	135&lt;br /&gt;
* 7.5.4.4	Defluoridation of Water	139&lt;br /&gt;
* 7.5.4.4.1	Fluorides	139&lt;br /&gt;
* 7.5.4.4.2	Defluoridation	139&lt;br /&gt;
* 7.5.4.5	Water Conditioning	141&lt;br /&gt;
* 7.5.5	Managemen&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=496</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=496"/>
		<updated>2020-03-30T19:14:57Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| Class=&amp;quot;Wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Apendices: Appendices]] || 231&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Chapter_One:_Introduction|CHAPTER ONE: INTRODUCTION]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[CHAPTER TWO: PROJECT PLANNING|CHAPTER TWO: PROJECT PLANNING]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[CHAPTER THREE: WATER SOURCES ANALYSIS|CHAPTER THREE: WATER SOURCES ANALYSIS]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[CHAPTER FOUR: WATER DEMAND ASSESSMENT|CHAPTER FOUR: WATER DEMAND ASSESSMENT]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[CHAPTER FIVE: PIPELINES DESIGN|CHAPTER FIVE: PIPELINES DESIGN]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[CHAPTER SIX: PUMPING SYSTEMS|CHAPTER SIX: PUMPING SYSTEMS]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[CHAPTER SEVEN: WATER TREATMENT|CHAPTER SEVEN: WATER TREATMENT]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[CHAPTER EIGHT: TREATMENT OF WATERS WITH SPECIAL CONTAMINANTS|CHAPTER EIGHT: TREATMENT OF WATERS WITH SPECIAL CONTAMINANTS]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[CHAPTER NINE: DESIGN OF WATER STRUCTURES|CHAPTER NINE: DESIGN OF WATER STRUCTURES]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[CHAPTER TEN: APPLICATION SOFTWARE|CHAPTER TEN: APPLICATION SOFTWARE]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[CHAPTER ELEVEN: METERING|CHAPTER ELEVEN: METERING]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[CHAPTER TWELVE: DESIGN STANDARDS AND SPECIFICATIONS|CHAPTER TWELVE: DESIGN STANDARDS AND SPECIFICATIONS]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[CHAPTER THIRTEEN: ROLE OF STAKEHOLDERS IN DESIGN OF WATER SUPPLY PROJECTS|CHAPTER THIRTEEN: ROLE OF STAKEHOLDERS IN DESIGN OF WATER SUPPLY PROJECTS]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[APENDICES: APPENDICES]] || 231&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| Class=&amp;quot;Wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Apendices: Appendices]] || 231&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Chapter #!! Chapter Title!! Page&lt;br /&gt;
|-&lt;br /&gt;
| i || LIST OF SPECIAL COMMITTEE MEMBERS || V&lt;br /&gt;
|-&lt;br /&gt;
| 1|| CHAPTER ONE: INTRODUCTION		 || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1|| Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.1 || Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.2 || Climate Change and Resilience to Climate Change || 2&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.3 || Public-Private Partnership in Water Supply and Sanitation Projects in Developing Countries || 3&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.4 || International Water Law || 4&lt;br /&gt;
|-&lt;br /&gt;
| 1.2 || Development Agenda and Water and Sanitation Sector in Tanzania || 5&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.1 || National Water Policy || 7&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.2|| Legal and Institutional Framework for Water Supply and Sanitation Services || 8&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.3 || Coverage and Access to Water Supply Services || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.4|| Policy Environment for Water and Sanitation Services in Tanzania || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.5 || Major Stakeholders in  Water Supply and Sanitation Projects || 10&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.6 || Water Supply and Sanitation Public Private Partnership in Tanzania || 11&lt;br /&gt;
|-&lt;br /&gt;
| 1.3 || Rationale for Preparation of the Fourth Edition DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.4 || About the Fourth Edition of the DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.5 || Organisation of the 4th edition of the DCOM Manual || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.6 || Purpose of this Volume || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.7 || References	 || 15&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
* CHAPTER TWO	17&lt;br /&gt;
* PROJECT PLANNING	17&lt;br /&gt;
* 2.1	Planning Considerations for Water Supply Projects	17&lt;br /&gt;
* 2.2	Project Planning Steps	18&lt;br /&gt;
* 2.3	Pump Protection	18&lt;br /&gt;
* 2.3.1	Initiation	18&lt;br /&gt;
* 2.3.1.1	Community Assessment Steps	20&lt;br /&gt;
* 2.3.1.2	Methods of conducting community assessment	20&lt;br /&gt;
* 2.3.1.2.1	Comprehensive community assessment	20&lt;br /&gt;
* 2.3.1.2.2	Strategic community assessment	20&lt;br /&gt;
* 2.3.2	Pre-feasibility Study	21&lt;br /&gt;
* 2.3.3	Feasibility Study	21&lt;br /&gt;
* 2.3.3.1	Water Supply Projects Ranking and Technology Selection Criteria	22&lt;br /&gt;
* 2.3.3.1.1	Ranking of Projects	22&lt;br /&gt;
* 2.3.3.1.2	Choice of Technology	23&lt;br /&gt;
* 2.3.4	Preliminary and Detailed Design	23&lt;br /&gt;
* 2.3.4.1	Detailed Engineering Drawings	24&lt;br /&gt;
* 2.3.4.2	Detailed estimates of capital costs	24&lt;br /&gt;
* 2.3.4.3	Detailed estimates of recurrent costs	24&lt;br /&gt;
* 2.3.4.4	Anticipated revenue	25&lt;br /&gt;
* 2.3.4.5	Detailed design report	25&lt;br /&gt;
* 2.3.4.6	Project write-up to be submitted to potential financiers	25&lt;br /&gt;
* 2.3.5	Project Phasing	25&lt;br /&gt;
* 2.3.6	Procurement	26&lt;br /&gt;
* 2.3.6.1	2.2.6.1 Preparation of Tender Documents	26&lt;br /&gt;
* 2.3.6.2	Tendering process	27&lt;br /&gt;
* 2.3.7	Implementation/Construction Stage	27&lt;br /&gt;
* 2.3.7.1	Contract Management	27&lt;br /&gt;
* 2.3.7.2	Contract supervision and administration	27&lt;br /&gt;
* 2.3.8	Operation and Maintenance Stage	28&lt;br /&gt;
* 2.3.9	Performance Monitoring	28&lt;br /&gt;
* 2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans	28&lt;br /&gt;
* 2.4.1	Status of Development and Implementation of IWRMD Plans	29&lt;br /&gt;
* 2.4.2	Components of IWRMD Plans	30&lt;br /&gt;
* 2.5	Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change	30&lt;br /&gt;
* 2.6	Environmental and Social Impact Assessment Compliance	30&lt;br /&gt;
* 2.6.1	Procedures for Conducting ESIA in Tanzania	31&lt;br /&gt;
* 2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance	31&lt;br /&gt;
* 2.7	Potential Impacts of Climate Change on Water Supply Projects	32&lt;br /&gt;
* 2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages	32&lt;br /&gt;
* 2.9	References	32&lt;br /&gt;
* CHAPTER THREE	35&lt;br /&gt;
* WATER SOURCES ANALYSIS	35&lt;br /&gt;
* 3.1	Availability of Water Resources in Tanzania Mainland	35&lt;br /&gt;
* 3.2	Water Sources Available in Tanzania Mainland	38&lt;br /&gt;
* 3.2.1	Rainwater and fog harvesting	39&lt;br /&gt;
* 3.2.2	Surface Water	39&lt;br /&gt;
* 3.2.2.1	Rivers or streams	39&lt;br /&gt;
* 3.2.2.2	Impoundments	39&lt;br /&gt;
* 3.2.2.3	Springs	39&lt;br /&gt;
* 3.2.2.4	Lakes	39&lt;br /&gt;
* 3.2.2.5	Dams	40&lt;br /&gt;
* 3.2.3	Groundwater	40&lt;br /&gt;
* 3.2.3.1	Infiltration galleries/wells	40&lt;br /&gt;
* 3.2.3.2	Well	40&lt;br /&gt;
* 3.2.3.3	Classification of wells based on the aquifer tapped	41&lt;br /&gt;
* 3.2.3.3.1	Shallow wells	41&lt;br /&gt;
* 3.2.3.3.2	Deep wells	41&lt;br /&gt;
* 3.2.3.3.3	Artesian wells	41&lt;br /&gt;
* 3.3	Quality Suitability of Water Sources for Water Supply Projects	42&lt;br /&gt;
* 3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment	42&lt;br /&gt;
* 3.5	General Considerations for Selection of Water Sources	42&lt;br /&gt;
* 3.5.1	Adequacy and reliability	42&lt;br /&gt;
* 3.5.2	Quality of water sources	43&lt;br /&gt;
* 3.5.3	Technical Requirements	43&lt;br /&gt;
* 3.5.4	Cost implications to develop a water source	43&lt;br /&gt;
* 3.5.5	Protection of water sources	43&lt;br /&gt;
* 3.5.6	Legal and management requirements	44&lt;br /&gt;
* 3.5.7	Distance of water supply source	44&lt;br /&gt;
* 3.5.8	Topography of the project area and its surroundings	44&lt;br /&gt;
* 3.5.9	Elevation of a source of water supply	44&lt;br /&gt;
* 3.6	Determination of water source yield	44&lt;br /&gt;
* 3.6.1	Rainwater and fog harvesting	45&lt;br /&gt;
* 3.6.1.1	Rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.1	Types of rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.2	Components of rainwater harvesting system	46&lt;br /&gt;
* 3.6.1.1.3	Estimation of the yield	47&lt;br /&gt;
* 3.6.2	Hydrological Analysis of Surface Waters	47&lt;br /&gt;
* 3.7	Other considerations for various water sources	55&lt;br /&gt;
* 3.7.1	Water permits Considerations	55&lt;br /&gt;
* 3.7.2	Conservation of water sources	55&lt;br /&gt;
* 3.8	References	55&lt;br /&gt;
* CHAPTER FOUR	56&lt;br /&gt;
* WATER DEMAND ASSESSMENT	56&lt;br /&gt;
* 4.1	Water Demand Assessment	56&lt;br /&gt;
* 4.2	General Factors Affecting Water Demand Assessment	57&lt;br /&gt;
* 4.3	Determination of Water Demand for Different Uses	58&lt;br /&gt;
* Step 7. Establish Net Water Demand	67&lt;br /&gt;
* Step 9: Establish Operational water consumption	67&lt;br /&gt;
* Step 10: Establish System water losses	68&lt;br /&gt;
* Step 11 Establish Non-Revenue Water	69&lt;br /&gt;
* 4.4	Variations in Water Consumption	70&lt;br /&gt;
* 4.4.1	Definitions	70&lt;br /&gt;
* 4.4.2	Variation in the Rate of Consumption	71&lt;br /&gt;
* 4.4.2.1	Diurnal variation in demand	71&lt;br /&gt;
* 4.4.3	Peak Factors	72&lt;br /&gt;
* 4.4.4	Predicting Demand	74&lt;br /&gt;
* 4.4.5	Design Demand	75&lt;br /&gt;
* 4.5	References	75&lt;br /&gt;
* CHAPTER FIVE	76&lt;br /&gt;
* PIPELINES DESIGN	76&lt;br /&gt;
* 5.1	Design Requirements of pipelines	76&lt;br /&gt;
* 5.2	Types of pipelines	76&lt;br /&gt;
* 5.3	Security considerations for pipelines	76&lt;br /&gt;
* 5.3.1	Methods of water transmission and distribution	76&lt;br /&gt;
* 5.3.2	Gravity flow	77&lt;br /&gt;
* 5.3.3	Pumping with storage	77&lt;br /&gt;
* 5.3.4	Direct pumping to the distribution system	77&lt;br /&gt;
* 5.4	Pipeline Hydraulics Assessment	77&lt;br /&gt;
* 5.4.1	Pressure	77&lt;br /&gt;
* 5.4.2	Determination of Head Losses	77&lt;br /&gt;
* 5.5	Water supply transmission system	79&lt;br /&gt;
* 5.5.1	Determination of Transmission Pipe Size	79&lt;br /&gt;
* 5.5.2	Maximum Pressure	79&lt;br /&gt;
* 5.6	Distribution system	80&lt;br /&gt;
* 5.6.1	Branched System	80&lt;br /&gt;
* 5.6.2	Looped System	81&lt;br /&gt;
* 5.7	Pipe network analysis	82&lt;br /&gt;
* 5.7.1	Network analysis by Conventional method (Hardy Cross)	82&lt;br /&gt;
* 5.7.2	Network Analysis by Computer Software	82&lt;br /&gt;
* 5.7.2.1	EPANET Software	82&lt;br /&gt;
* 5.7.3	Pipeline design criteria	85&lt;br /&gt;
* 5.8	Pipeline materials selection	86&lt;br /&gt;
* 5.8.1	Considerations in Selecting Pipeline Materials	86&lt;br /&gt;
* 5.8.1.1	Flow Characteristics	86&lt;br /&gt;
* 5.8.1.2	Pipe Strength	86&lt;br /&gt;
* 5.8.1.3	Durability	87&lt;br /&gt;
* 5.8.1.4	Type of Soil	87&lt;br /&gt;
* 5.8.1.5	Availability	87&lt;br /&gt;
* 5.8.1.6	Cost of Pipes	87&lt;br /&gt;
* 5.8.2	Types of Pipe Materials Available	87&lt;br /&gt;
* 5.8.2.1	Galvanized Iron (GI) Pipes	87&lt;br /&gt;
* 5.8.2.2	Plastic Pipes	87&lt;br /&gt;
* 5.9	Appurtenances for transmission and distribution mains	88&lt;br /&gt;
* 5.9.1	Valves	89&lt;br /&gt;
* 5.9.1.1	Isolation Valves	89&lt;br /&gt;
* 5.9.1.2	Check Valves	89&lt;br /&gt;
* 5.9.1.3	Float Valves	89&lt;br /&gt;
* 5.9.1.4	Air Release Valves	89&lt;br /&gt;
* 5.9.1.5	Pressure Reducing Valves	89&lt;br /&gt;
* 5.9.1.6	Washout valves	89&lt;br /&gt;
* 5.9.2	Fittings	89&lt;br /&gt;
* 5.10	References	90&lt;br /&gt;
* CHAPTER SIX	91&lt;br /&gt;
* PUMPING SYSTEMS	91&lt;br /&gt;
* 6.1	Introduction	91&lt;br /&gt;
* 6.2	Rationale	91&lt;br /&gt;
* 6.3	Common Types of Pumps used in water supply	91&lt;br /&gt;
* 6.4	Pumping System Setup	91&lt;br /&gt;
* 6.5	Source of Pumping Power	92&lt;br /&gt;
* 6.6	Pumping system design pump selection	92&lt;br /&gt;
* 6.7	Pump Protection	95&lt;br /&gt;
* 6.8	References	95&lt;br /&gt;
* CHAPTER SEVEN	96&lt;br /&gt;
* WATER TREATMENT	96&lt;br /&gt;
* 7.1	Introduction	96&lt;br /&gt;
* 7.1.1	Classification of the qualities of water sources found in Tanzania according to the complexity of its treatment	96&lt;br /&gt;
* 7.1.2	Classification of Unit Operations to achieve water treatment levels	99&lt;br /&gt;
* 7.2	Recommended overall design approach for treatment plant components	99&lt;br /&gt;
* 7.3	Documents and websites consulted and those which are hyper-linked to the DCOM Manual	100&lt;br /&gt;
* 7.4	Water treatment design considerations	100&lt;br /&gt;
* 7.5	Water treatment levels and units	101&lt;br /&gt;
* 7.5.1	Pre-treatment	101&lt;br /&gt;
* 7.5.1.1	Scum and Floating Materials Skimmer	101&lt;br /&gt;
* 7.5.1.2	Screening or straining	101&lt;br /&gt;
* 7.5.1.3	Grit Removal	103&lt;br /&gt;
* 7.5.1.3.1	Design criteria	103&lt;br /&gt;
* 7.5.1.4	Sand Traps	105&lt;br /&gt;
* 7.5.1.5	Pre-chlorination	107&lt;br /&gt;
* 7.5.1.6	Water pre-conditioning (pH adjustment)	108&lt;br /&gt;
* 7.5.2	Primary Treatment	108&lt;br /&gt;
* 7.5.2.1	Sedimentation	108&lt;br /&gt;
* 7.5.2.2	Primary Filtration	114&lt;br /&gt;
* 7.5.2.2.1	Slow Sand Filtration	114&lt;br /&gt;
* 7.5.2.2.2	Rapid Gravity Sand Filtration	117&lt;br /&gt;
* 7.5.2.2.3	Comparison between Slow Sand Filters and Rapid Sand Filters	118&lt;br /&gt;
* 7.5.2.2.4	Other Types of Filters	119&lt;br /&gt;
* 7.5.2.3	Floatation	124&lt;br /&gt;
* 7.5.2.3.1	Dissolved-Air Floatation	124&lt;br /&gt;
* 7.5.2.3.2	Electrolytic Floatation	125&lt;br /&gt;
* 7.5.2.3.3	Dispersed-Air Floatation	125&lt;br /&gt;
* 7.5.2.4	Aeration	125&lt;br /&gt;
* 7.5.2.4.1	Falling Water Aerators	126&lt;br /&gt;
* 7.5.2.4.2	Spray Aerators	127&lt;br /&gt;
* 7.5.3	Secondary Treatment	130&lt;br /&gt;
* 7.5.3.1	Clarification	130&lt;br /&gt;
* 7.5.3.2	Coagulation	130&lt;br /&gt;
* 7.5.3.3	Flocculation	131&lt;br /&gt;
* 7.5.3.4	Filtration	131&lt;br /&gt;
* 7.5.4	Tertiary Treatment	132&lt;br /&gt;
* 7.5.4.1	Disinfection	132&lt;br /&gt;
* 7.5.4.1.1	Disinfection Methods	132&lt;br /&gt;
* 7.5.4.1.2	Chlorinators	132&lt;br /&gt;
* 7.5.4.1.3	Design considerations for chlorinators	133&lt;br /&gt;
* 7.5.4.2	Ozonation	133&lt;br /&gt;
* 7.5.4.3	Water softening	134&lt;br /&gt;
* 7.5.4.3.1	Methods of Softening	135&lt;br /&gt;
* 7.5.4.4	Defluoridation of Water	139&lt;br /&gt;
* 7.5.4.4.1	Fluorides	139&lt;br /&gt;
* 7.5.4.4.2	Defluoridation	139&lt;br /&gt;
* 7.5.4.5	Water Conditioning	141&lt;br /&gt;
* 7.5.5	Managemen&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=495</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=495"/>
		<updated>2020-03-30T19:13:26Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| Class=&amp;quot;Wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Chapter_One:_Introduction|Chapter One: Introduction]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[Chapter Two: Project Planning|Chapter Two: Project Planning]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[Chapter Three: Water Sources Analysis|Chapter Three: Water Sources Analysis]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[Chapter Four: Water Demand Assessment|Chapter Four: Water Demand Assessment]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[Chapter Five: Pipelines Design|Chapter Five: Pipelines Design]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[Chapter Six: Pumping Systems|Chapter Six: Pumping Systems]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[Chapter Seven: Water Treatment|Chapter Seven: Water Treatment]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[Chapter Eight: Treatment of Waters With Special Contaminants|Chapter Eight: Treatment of Waters With Special Contaminants]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[Chapter Nine: Design of Water Structures|Chapter Nine: Design of Water Structures]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[Chapter Ten: Application Software|Chapter Ten: Application Software]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[Chapter Eleven: Metering|Chapter Eleven: Metering]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[Chapter Twelve: Design Standards and Specifications|Chapter Twelve: Design Standards and Specifications]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects|Chapter Thirteen: Role of Stakeholders in Design of Water Supply Projects]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[Apendices: Appendices]] || 231&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Chapter_One:_Introduction|CHAPTER ONE: INTRODUCTION]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[CHAPTER TWO: PROJECT PLANNING|CHAPTER TWO: PROJECT PLANNING]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[CHAPTER THREE: WATER SOURCES ANALYSIS|CHAPTER THREE: WATER SOURCES ANALYSIS]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[CHAPTER FOUR: WATER DEMAND ASSESSMENT|CHAPTER FOUR: WATER DEMAND ASSESSMENT]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[CHAPTER FIVE: PIPELINES DESIGN|CHAPTER FIVE: PIPELINES DESIGN]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[CHAPTER SIX: PUMPING SYSTEMS|CHAPTER SIX: PUMPING SYSTEMS]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[CHAPTER SEVEN: WATER TREATMENT|CHAPTER SEVEN: WATER TREATMENT]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[CHAPTER EIGHT: TREATMENT OF WATERS WITH SPECIAL CONTAMINANTS|CHAPTER EIGHT: TREATMENT OF WATERS WITH SPECIAL CONTAMINANTS]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[CHAPTER NINE: DESIGN OF WATER STRUCTURES|CHAPTER NINE: DESIGN OF WATER STRUCTURES]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[CHAPTER TEN: APPLICATION SOFTWARE|CHAPTER TEN: APPLICATION SOFTWARE]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[CHAPTER ELEVEN: METERING|CHAPTER ELEVEN: METERING]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[CHAPTER TWELVE: DESIGN STANDARDS AND SPECIFICATIONS|CHAPTER TWELVE: DESIGN STANDARDS AND SPECIFICATIONS]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[CHAPTER THIRTEEN: ROLE OF STAKEHOLDERS IN DESIGN OF WATER SUPPLY PROJECTS|CHAPTER THIRTEEN: ROLE OF STAKEHOLDERS IN DESIGN OF WATER SUPPLY PROJECTS]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[APENDICES: APPENDICES]] || 231&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Chapter #!! Chapter Title!! Page&lt;br /&gt;
|-&lt;br /&gt;
| i || LIST OF SPECIAL COMMITTEE MEMBERS || V&lt;br /&gt;
|-&lt;br /&gt;
| 1|| CHAPTER ONE: INTRODUCTION		 || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1|| Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.1 || Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.2 || Climate Change and Resilience to Climate Change || 2&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.3 || Public-Private Partnership in Water Supply and Sanitation Projects in Developing Countries || 3&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.4 || International Water Law || 4&lt;br /&gt;
|-&lt;br /&gt;
| 1.2 || Development Agenda and Water and Sanitation Sector in Tanzania || 5&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.1 || National Water Policy || 7&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.2|| Legal and Institutional Framework for Water Supply and Sanitation Services || 8&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.3 || Coverage and Access to Water Supply Services || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.4|| Policy Environment for Water and Sanitation Services in Tanzania || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.5 || Major Stakeholders in  Water Supply and Sanitation Projects || 10&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.6 || Water Supply and Sanitation Public Private Partnership in Tanzania || 11&lt;br /&gt;
|-&lt;br /&gt;
| 1.3 || Rationale for Preparation of the Fourth Edition DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.4 || About the Fourth Edition of the DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.5 || Organisation of the 4th edition of the DCOM Manual || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.6 || Purpose of this Volume || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.7 || References	 || 15&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
* CHAPTER TWO	17&lt;br /&gt;
* PROJECT PLANNING	17&lt;br /&gt;
* 2.1	Planning Considerations for Water Supply Projects	17&lt;br /&gt;
* 2.2	Project Planning Steps	18&lt;br /&gt;
* 2.3	Pump Protection	18&lt;br /&gt;
* 2.3.1	Initiation	18&lt;br /&gt;
* 2.3.1.1	Community Assessment Steps	20&lt;br /&gt;
* 2.3.1.2	Methods of conducting community assessment	20&lt;br /&gt;
* 2.3.1.2.1	Comprehensive community assessment	20&lt;br /&gt;
* 2.3.1.2.2	Strategic community assessment	20&lt;br /&gt;
* 2.3.2	Pre-feasibility Study	21&lt;br /&gt;
* 2.3.3	Feasibility Study	21&lt;br /&gt;
* 2.3.3.1	Water Supply Projects Ranking and Technology Selection Criteria	22&lt;br /&gt;
* 2.3.3.1.1	Ranking of Projects	22&lt;br /&gt;
* 2.3.3.1.2	Choice of Technology	23&lt;br /&gt;
* 2.3.4	Preliminary and Detailed Design	23&lt;br /&gt;
* 2.3.4.1	Detailed Engineering Drawings	24&lt;br /&gt;
* 2.3.4.2	Detailed estimates of capital costs	24&lt;br /&gt;
* 2.3.4.3	Detailed estimates of recurrent costs	24&lt;br /&gt;
* 2.3.4.4	Anticipated revenue	25&lt;br /&gt;
* 2.3.4.5	Detailed design report	25&lt;br /&gt;
* 2.3.4.6	Project write-up to be submitted to potential financiers	25&lt;br /&gt;
* 2.3.5	Project Phasing	25&lt;br /&gt;
* 2.3.6	Procurement	26&lt;br /&gt;
* 2.3.6.1	2.2.6.1 Preparation of Tender Documents	26&lt;br /&gt;
* 2.3.6.2	Tendering process	27&lt;br /&gt;
* 2.3.7	Implementation/Construction Stage	27&lt;br /&gt;
* 2.3.7.1	Contract Management	27&lt;br /&gt;
* 2.3.7.2	Contract supervision and administration	27&lt;br /&gt;
* 2.3.8	Operation and Maintenance Stage	28&lt;br /&gt;
* 2.3.9	Performance Monitoring	28&lt;br /&gt;
* 2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans	28&lt;br /&gt;
* 2.4.1	Status of Development and Implementation of IWRMD Plans	29&lt;br /&gt;
* 2.4.2	Components of IWRMD Plans	30&lt;br /&gt;
* 2.5	Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change	30&lt;br /&gt;
* 2.6	Environmental and Social Impact Assessment Compliance	30&lt;br /&gt;
* 2.6.1	Procedures for Conducting ESIA in Tanzania	31&lt;br /&gt;
* 2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance	31&lt;br /&gt;
* 2.7	Potential Impacts of Climate Change on Water Supply Projects	32&lt;br /&gt;
* 2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages	32&lt;br /&gt;
* 2.9	References	32&lt;br /&gt;
* CHAPTER THREE	35&lt;br /&gt;
* WATER SOURCES ANALYSIS	35&lt;br /&gt;
* 3.1	Availability of Water Resources in Tanzania Mainland	35&lt;br /&gt;
* 3.2	Water Sources Available in Tanzania Mainland	38&lt;br /&gt;
* 3.2.1	Rainwater and fog harvesting	39&lt;br /&gt;
* 3.2.2	Surface Water	39&lt;br /&gt;
* 3.2.2.1	Rivers or streams	39&lt;br /&gt;
* 3.2.2.2	Impoundments	39&lt;br /&gt;
* 3.2.2.3	Springs	39&lt;br /&gt;
* 3.2.2.4	Lakes	39&lt;br /&gt;
* 3.2.2.5	Dams	40&lt;br /&gt;
* 3.2.3	Groundwater	40&lt;br /&gt;
* 3.2.3.1	Infiltration galleries/wells	40&lt;br /&gt;
* 3.2.3.2	Well	40&lt;br /&gt;
* 3.2.3.3	Classification of wells based on the aquifer tapped	41&lt;br /&gt;
* 3.2.3.3.1	Shallow wells	41&lt;br /&gt;
* 3.2.3.3.2	Deep wells	41&lt;br /&gt;
* 3.2.3.3.3	Artesian wells	41&lt;br /&gt;
* 3.3	Quality Suitability of Water Sources for Water Supply Projects	42&lt;br /&gt;
* 3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment	42&lt;br /&gt;
* 3.5	General Considerations for Selection of Water Sources	42&lt;br /&gt;
* 3.5.1	Adequacy and reliability	42&lt;br /&gt;
* 3.5.2	Quality of water sources	43&lt;br /&gt;
* 3.5.3	Technical Requirements	43&lt;br /&gt;
* 3.5.4	Cost implications to develop a water source	43&lt;br /&gt;
* 3.5.5	Protection of water sources	43&lt;br /&gt;
* 3.5.6	Legal and management requirements	44&lt;br /&gt;
* 3.5.7	Distance of water supply source	44&lt;br /&gt;
* 3.5.8	Topography of the project area and its surroundings	44&lt;br /&gt;
* 3.5.9	Elevation of a source of water supply	44&lt;br /&gt;
* 3.6	Determination of water source yield	44&lt;br /&gt;
* 3.6.1	Rainwater and fog harvesting	45&lt;br /&gt;
* 3.6.1.1	Rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.1	Types of rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.2	Components of rainwater harvesting system	46&lt;br /&gt;
* 3.6.1.1.3	Estimation of the yield	47&lt;br /&gt;
* 3.6.2	Hydrological Analysis of Surface Waters	47&lt;br /&gt;
* 3.7	Other considerations for various water sources	55&lt;br /&gt;
* 3.7.1	Water permits Considerations	55&lt;br /&gt;
* 3.7.2	Conservation of water sources	55&lt;br /&gt;
* 3.8	References	55&lt;br /&gt;
* CHAPTER FOUR	56&lt;br /&gt;
* WATER DEMAND ASSESSMENT	56&lt;br /&gt;
* 4.1	Water Demand Assessment	56&lt;br /&gt;
* 4.2	General Factors Affecting Water Demand Assessment	57&lt;br /&gt;
* 4.3	Determination of Water Demand for Different Uses	58&lt;br /&gt;
* Step 7. Establish Net Water Demand	67&lt;br /&gt;
* Step 9: Establish Operational water consumption	67&lt;br /&gt;
* Step 10: Establish System water losses	68&lt;br /&gt;
* Step 11 Establish Non-Revenue Water	69&lt;br /&gt;
* 4.4	Variations in Water Consumption	70&lt;br /&gt;
* 4.4.1	Definitions	70&lt;br /&gt;
* 4.4.2	Variation in the Rate of Consumption	71&lt;br /&gt;
* 4.4.2.1	Diurnal variation in demand	71&lt;br /&gt;
* 4.4.3	Peak Factors	72&lt;br /&gt;
* 4.4.4	Predicting Demand	74&lt;br /&gt;
* 4.4.5	Design Demand	75&lt;br /&gt;
* 4.5	References	75&lt;br /&gt;
* CHAPTER FIVE	76&lt;br /&gt;
* PIPELINES DESIGN	76&lt;br /&gt;
* 5.1	Design Requirements of pipelines	76&lt;br /&gt;
* 5.2	Types of pipelines	76&lt;br /&gt;
* 5.3	Security considerations for pipelines	76&lt;br /&gt;
* 5.3.1	Methods of water transmission and distribution	76&lt;br /&gt;
* 5.3.2	Gravity flow	77&lt;br /&gt;
* 5.3.3	Pumping with storage	77&lt;br /&gt;
* 5.3.4	Direct pumping to the distribution system	77&lt;br /&gt;
* 5.4	Pipeline Hydraulics Assessment	77&lt;br /&gt;
* 5.4.1	Pressure	77&lt;br /&gt;
* 5.4.2	Determination of Head Losses	77&lt;br /&gt;
* 5.5	Water supply transmission system	79&lt;br /&gt;
* 5.5.1	Determination of Transmission Pipe Size	79&lt;br /&gt;
* 5.5.2	Maximum Pressure	79&lt;br /&gt;
* 5.6	Distribution system	80&lt;br /&gt;
* 5.6.1	Branched System	80&lt;br /&gt;
* 5.6.2	Looped System	81&lt;br /&gt;
* 5.7	Pipe network analysis	82&lt;br /&gt;
* 5.7.1	Network analysis by Conventional method (Hardy Cross)	82&lt;br /&gt;
* 5.7.2	Network Analysis by Computer Software	82&lt;br /&gt;
* 5.7.2.1	EPANET Software	82&lt;br /&gt;
* 5.7.3	Pipeline design criteria	85&lt;br /&gt;
* 5.8	Pipeline materials selection	86&lt;br /&gt;
* 5.8.1	Considerations in Selecting Pipeline Materials	86&lt;br /&gt;
* 5.8.1.1	Flow Characteristics	86&lt;br /&gt;
* 5.8.1.2	Pipe Strength	86&lt;br /&gt;
* 5.8.1.3	Durability	87&lt;br /&gt;
* 5.8.1.4	Type of Soil	87&lt;br /&gt;
* 5.8.1.5	Availability	87&lt;br /&gt;
* 5.8.1.6	Cost of Pipes	87&lt;br /&gt;
* 5.8.2	Types of Pipe Materials Available	87&lt;br /&gt;
* 5.8.2.1	Galvanized Iron (GI) Pipes	87&lt;br /&gt;
* 5.8.2.2	Plastic Pipes	87&lt;br /&gt;
* 5.9	Appurtenances for transmission and distribution mains	88&lt;br /&gt;
* 5.9.1	Valves	89&lt;br /&gt;
* 5.9.1.1	Isolation Valves	89&lt;br /&gt;
* 5.9.1.2	Check Valves	89&lt;br /&gt;
* 5.9.1.3	Float Valves	89&lt;br /&gt;
* 5.9.1.4	Air Release Valves	89&lt;br /&gt;
* 5.9.1.5	Pressure Reducing Valves	89&lt;br /&gt;
* 5.9.1.6	Washout valves	89&lt;br /&gt;
* 5.9.2	Fittings	89&lt;br /&gt;
* 5.10	References	90&lt;br /&gt;
* CHAPTER SIX	91&lt;br /&gt;
* PUMPING SYSTEMS	91&lt;br /&gt;
* 6.1	Introduction	91&lt;br /&gt;
* 6.2	Rationale	91&lt;br /&gt;
* 6.3	Common Types of Pumps used in water supply	91&lt;br /&gt;
* 6.4	Pumping System Setup	91&lt;br /&gt;
* 6.5	Source of Pumping Power	92&lt;br /&gt;
* 6.6	Pumping system design pump selection	92&lt;br /&gt;
* 6.7	Pump Protection	95&lt;br /&gt;
* 6.8	References	95&lt;br /&gt;
* CHAPTER SEVEN	96&lt;br /&gt;
* WATER TREATMENT	96&lt;br /&gt;
* 7.1	Introduction	96&lt;br /&gt;
* 7.1.1	Classification of the qualities of water sources found in Tanzania according to the complexity of its treatment	96&lt;br /&gt;
* 7.1.2	Classification of Unit Operations to achieve water treatment levels	99&lt;br /&gt;
* 7.2	Recommended overall design approach for treatment plant components	99&lt;br /&gt;
* 7.3	Documents and websites consulted and those which are hyper-linked to the DCOM Manual	100&lt;br /&gt;
* 7.4	Water treatment design considerations	100&lt;br /&gt;
* 7.5	Water treatment levels and units	101&lt;br /&gt;
* 7.5.1	Pre-treatment	101&lt;br /&gt;
* 7.5.1.1	Scum and Floating Materials Skimmer	101&lt;br /&gt;
* 7.5.1.2	Screening or straining	101&lt;br /&gt;
* 7.5.1.3	Grit Removal	103&lt;br /&gt;
* 7.5.1.3.1	Design criteria	103&lt;br /&gt;
* 7.5.1.4	Sand Traps	105&lt;br /&gt;
* 7.5.1.5	Pre-chlorination	107&lt;br /&gt;
* 7.5.1.6	Water pre-conditioning (pH adjustment)	108&lt;br /&gt;
* 7.5.2	Primary Treatment	108&lt;br /&gt;
* 7.5.2.1	Sedimentation	108&lt;br /&gt;
* 7.5.2.2	Primary Filtration	114&lt;br /&gt;
* 7.5.2.2.1	Slow Sand Filtration	114&lt;br /&gt;
* 7.5.2.2.2	Rapid Gravity Sand Filtration	117&lt;br /&gt;
* 7.5.2.2.3	Comparison between Slow Sand Filters and Rapid Sand Filters	118&lt;br /&gt;
* 7.5.2.2.4	Other Types of Filters	119&lt;br /&gt;
* 7.5.2.3	Floatation	124&lt;br /&gt;
* 7.5.2.3.1	Dissolved-Air Floatation	124&lt;br /&gt;
* 7.5.2.3.2	Electrolytic Floatation	125&lt;br /&gt;
* 7.5.2.3.3	Dispersed-Air Floatation	125&lt;br /&gt;
* 7.5.2.4	Aeration	125&lt;br /&gt;
* 7.5.2.4.1	Falling Water Aerators	126&lt;br /&gt;
* 7.5.2.4.2	Spray Aerators	127&lt;br /&gt;
* 7.5.3	Secondary Treatment	130&lt;br /&gt;
* 7.5.3.1	Clarification	130&lt;br /&gt;
* 7.5.3.2	Coagulation	130&lt;br /&gt;
* 7.5.3.3	Flocculation	131&lt;br /&gt;
* 7.5.3.4	Filtration	131&lt;br /&gt;
* 7.5.4	Tertiary Treatment	132&lt;br /&gt;
* 7.5.4.1	Disinfection	132&lt;br /&gt;
* 7.5.4.1.1	Disinfection Methods	132&lt;br /&gt;
* 7.5.4.1.2	Chlorinators	132&lt;br /&gt;
* 7.5.4.1.3	Design considerations for chlorinators	133&lt;br /&gt;
* 7.5.4.2	Ozonation	133&lt;br /&gt;
* 7.5.4.3	Water softening	134&lt;br /&gt;
* 7.5.4.3.1	Methods of Softening	135&lt;br /&gt;
* 7.5.4.4	Defluoridation of Water	139&lt;br /&gt;
* 7.5.4.4.1	Fluorides	139&lt;br /&gt;
* 7.5.4.4.2	Defluoridation	139&lt;br /&gt;
* 7.5.4.5	Water Conditioning	141&lt;br /&gt;
* 7.5.5	Managemen&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=494</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=494"/>
		<updated>2020-03-30T19:10:19Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Chapter_One:_Introduction|CHAPTER ONE: INTRODUCTION]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[CHAPTER TWO: PROJECT PLANNING|CHAPTER TWO: PROJECT PLANNING]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[CHAPTER THREE: WATER SOURCES ANALYSIS|CHAPTER THREE: WATER SOURCES ANALYSIS]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[CHAPTER FOUR: WATER DEMAND ASSESSMENT|CHAPTER FOUR: WATER DEMAND ASSESSMENT]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[CHAPTER FIVE: PIPELINES DESIGN|CHAPTER FIVE: PIPELINES DESIGN]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[CHAPTER SIX: PUMPING SYSTEMS|CHAPTER SIX: PUMPING SYSTEMS]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[CHAPTER SEVEN: WATER TREATMENT|CHAPTER SEVEN: WATER TREATMENT]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[CHAPTER EIGHT: TREATMENT OF WATERS WITH SPECIAL CONTAMINANTS|CHAPTER EIGHT: TREATMENT OF WATERS WITH SPECIAL CONTAMINANTS]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[CHAPTER NINE: DESIGN OF WATER STRUCTURES|CHAPTER NINE: DESIGN OF WATER STRUCTURES]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[CHAPTER TEN: APPLICATION SOFTWARE|CHAPTER TEN: APPLICATION SOFTWARE]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[CHAPTER ELEVEN: METERING|CHAPTER ELEVEN: METERING]] || 208&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[CHAPTER TWELVE: DESIGN STANDARDS AND SPECIFICATIONS|CHAPTER TWELVE: DESIGN STANDARDS AND SPECIFICATIONS]] || 217&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[CHAPTER THIRTEEN: ROLE OF STAKEHOLDERS IN DESIGN OF WATER SUPPLY PROJECTS|CHAPTER THIRTEEN: ROLE OF STAKEHOLDERS IN DESIGN OF WATER SUPPLY PROJECTS]] || 228&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[APENDICES: APPENDICES]] || 231&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Chapter #!! Chapter Title!! Page&lt;br /&gt;
|-&lt;br /&gt;
| i || LIST OF SPECIAL COMMITTEE MEMBERS || V&lt;br /&gt;
|-&lt;br /&gt;
| 1|| CHAPTER ONE: INTRODUCTION		 || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1|| Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.1 || Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.2 || Climate Change and Resilience to Climate Change || 2&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.3 || Public-Private Partnership in Water Supply and Sanitation Projects in Developing Countries || 3&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.4 || International Water Law || 4&lt;br /&gt;
|-&lt;br /&gt;
| 1.2 || Development Agenda and Water and Sanitation Sector in Tanzania || 5&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.1 || National Water Policy || 7&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.2|| Legal and Institutional Framework for Water Supply and Sanitation Services || 8&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.3 || Coverage and Access to Water Supply Services || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.4|| Policy Environment for Water and Sanitation Services in Tanzania || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.5 || Major Stakeholders in  Water Supply and Sanitation Projects || 10&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.6 || Water Supply and Sanitation Public Private Partnership in Tanzania || 11&lt;br /&gt;
|-&lt;br /&gt;
| 1.3 || Rationale for Preparation of the Fourth Edition DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.4 || About the Fourth Edition of the DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.5 || Organisation of the 4th edition of the DCOM Manual || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.6 || Purpose of this Volume || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.7 || References	 || 15&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
* CHAPTER TWO	17&lt;br /&gt;
* PROJECT PLANNING	17&lt;br /&gt;
* 2.1	Planning Considerations for Water Supply Projects	17&lt;br /&gt;
* 2.2	Project Planning Steps	18&lt;br /&gt;
* 2.3	Pump Protection	18&lt;br /&gt;
* 2.3.1	Initiation	18&lt;br /&gt;
* 2.3.1.1	Community Assessment Steps	20&lt;br /&gt;
* 2.3.1.2	Methods of conducting community assessment	20&lt;br /&gt;
* 2.3.1.2.1	Comprehensive community assessment	20&lt;br /&gt;
* 2.3.1.2.2	Strategic community assessment	20&lt;br /&gt;
* 2.3.2	Pre-feasibility Study	21&lt;br /&gt;
* 2.3.3	Feasibility Study	21&lt;br /&gt;
* 2.3.3.1	Water Supply Projects Ranking and Technology Selection Criteria	22&lt;br /&gt;
* 2.3.3.1.1	Ranking of Projects	22&lt;br /&gt;
* 2.3.3.1.2	Choice of Technology	23&lt;br /&gt;
* 2.3.4	Preliminary and Detailed Design	23&lt;br /&gt;
* 2.3.4.1	Detailed Engineering Drawings	24&lt;br /&gt;
* 2.3.4.2	Detailed estimates of capital costs	24&lt;br /&gt;
* 2.3.4.3	Detailed estimates of recurrent costs	24&lt;br /&gt;
* 2.3.4.4	Anticipated revenue	25&lt;br /&gt;
* 2.3.4.5	Detailed design report	25&lt;br /&gt;
* 2.3.4.6	Project write-up to be submitted to potential financiers	25&lt;br /&gt;
* 2.3.5	Project Phasing	25&lt;br /&gt;
* 2.3.6	Procurement	26&lt;br /&gt;
* 2.3.6.1	2.2.6.1 Preparation of Tender Documents	26&lt;br /&gt;
* 2.3.6.2	Tendering process	27&lt;br /&gt;
* 2.3.7	Implementation/Construction Stage	27&lt;br /&gt;
* 2.3.7.1	Contract Management	27&lt;br /&gt;
* 2.3.7.2	Contract supervision and administration	27&lt;br /&gt;
* 2.3.8	Operation and Maintenance Stage	28&lt;br /&gt;
* 2.3.9	Performance Monitoring	28&lt;br /&gt;
* 2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans	28&lt;br /&gt;
* 2.4.1	Status of Development and Implementation of IWRMD Plans	29&lt;br /&gt;
* 2.4.2	Components of IWRMD Plans	30&lt;br /&gt;
* 2.5	Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change	30&lt;br /&gt;
* 2.6	Environmental and Social Impact Assessment Compliance	30&lt;br /&gt;
* 2.6.1	Procedures for Conducting ESIA in Tanzania	31&lt;br /&gt;
* 2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance	31&lt;br /&gt;
* 2.7	Potential Impacts of Climate Change on Water Supply Projects	32&lt;br /&gt;
* 2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages	32&lt;br /&gt;
* 2.9	References	32&lt;br /&gt;
* CHAPTER THREE	35&lt;br /&gt;
* WATER SOURCES ANALYSIS	35&lt;br /&gt;
* 3.1	Availability of Water Resources in Tanzania Mainland	35&lt;br /&gt;
* 3.2	Water Sources Available in Tanzania Mainland	38&lt;br /&gt;
* 3.2.1	Rainwater and fog harvesting	39&lt;br /&gt;
* 3.2.2	Surface Water	39&lt;br /&gt;
* 3.2.2.1	Rivers or streams	39&lt;br /&gt;
* 3.2.2.2	Impoundments	39&lt;br /&gt;
* 3.2.2.3	Springs	39&lt;br /&gt;
* 3.2.2.4	Lakes	39&lt;br /&gt;
* 3.2.2.5	Dams	40&lt;br /&gt;
* 3.2.3	Groundwater	40&lt;br /&gt;
* 3.2.3.1	Infiltration galleries/wells	40&lt;br /&gt;
* 3.2.3.2	Well	40&lt;br /&gt;
* 3.2.3.3	Classification of wells based on the aquifer tapped	41&lt;br /&gt;
* 3.2.3.3.1	Shallow wells	41&lt;br /&gt;
* 3.2.3.3.2	Deep wells	41&lt;br /&gt;
* 3.2.3.3.3	Artesian wells	41&lt;br /&gt;
* 3.3	Quality Suitability of Water Sources for Water Supply Projects	42&lt;br /&gt;
* 3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment	42&lt;br /&gt;
* 3.5	General Considerations for Selection of Water Sources	42&lt;br /&gt;
* 3.5.1	Adequacy and reliability	42&lt;br /&gt;
* 3.5.2	Quality of water sources	43&lt;br /&gt;
* 3.5.3	Technical Requirements	43&lt;br /&gt;
* 3.5.4	Cost implications to develop a water source	43&lt;br /&gt;
* 3.5.5	Protection of water sources	43&lt;br /&gt;
* 3.5.6	Legal and management requirements	44&lt;br /&gt;
* 3.5.7	Distance of water supply source	44&lt;br /&gt;
* 3.5.8	Topography of the project area and its surroundings	44&lt;br /&gt;
* 3.5.9	Elevation of a source of water supply	44&lt;br /&gt;
* 3.6	Determination of water source yield	44&lt;br /&gt;
* 3.6.1	Rainwater and fog harvesting	45&lt;br /&gt;
* 3.6.1.1	Rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.1	Types of rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.2	Components of rainwater harvesting system	46&lt;br /&gt;
* 3.6.1.1.3	Estimation of the yield	47&lt;br /&gt;
* 3.6.2	Hydrological Analysis of Surface Waters	47&lt;br /&gt;
* 3.7	Other considerations for various water sources	55&lt;br /&gt;
* 3.7.1	Water permits Considerations	55&lt;br /&gt;
* 3.7.2	Conservation of water sources	55&lt;br /&gt;
* 3.8	References	55&lt;br /&gt;
* CHAPTER FOUR	56&lt;br /&gt;
* WATER DEMAND ASSESSMENT	56&lt;br /&gt;
* 4.1	Water Demand Assessment	56&lt;br /&gt;
* 4.2	General Factors Affecting Water Demand Assessment	57&lt;br /&gt;
* 4.3	Determination of Water Demand for Different Uses	58&lt;br /&gt;
* Step 7. Establish Net Water Demand	67&lt;br /&gt;
* Step 9: Establish Operational water consumption	67&lt;br /&gt;
* Step 10: Establish System water losses	68&lt;br /&gt;
* Step 11 Establish Non-Revenue Water	69&lt;br /&gt;
* 4.4	Variations in Water Consumption	70&lt;br /&gt;
* 4.4.1	Definitions	70&lt;br /&gt;
* 4.4.2	Variation in the Rate of Consumption	71&lt;br /&gt;
* 4.4.2.1	Diurnal variation in demand	71&lt;br /&gt;
* 4.4.3	Peak Factors	72&lt;br /&gt;
* 4.4.4	Predicting Demand	74&lt;br /&gt;
* 4.4.5	Design Demand	75&lt;br /&gt;
* 4.5	References	75&lt;br /&gt;
* CHAPTER FIVE	76&lt;br /&gt;
* PIPELINES DESIGN	76&lt;br /&gt;
* 5.1	Design Requirements of pipelines	76&lt;br /&gt;
* 5.2	Types of pipelines	76&lt;br /&gt;
* 5.3	Security considerations for pipelines	76&lt;br /&gt;
* 5.3.1	Methods of water transmission and distribution	76&lt;br /&gt;
* 5.3.2	Gravity flow	77&lt;br /&gt;
* 5.3.3	Pumping with storage	77&lt;br /&gt;
* 5.3.4	Direct pumping to the distribution system	77&lt;br /&gt;
* 5.4	Pipeline Hydraulics Assessment	77&lt;br /&gt;
* 5.4.1	Pressure	77&lt;br /&gt;
* 5.4.2	Determination of Head Losses	77&lt;br /&gt;
* 5.5	Water supply transmission system	79&lt;br /&gt;
* 5.5.1	Determination of Transmission Pipe Size	79&lt;br /&gt;
* 5.5.2	Maximum Pressure	79&lt;br /&gt;
* 5.6	Distribution system	80&lt;br /&gt;
* 5.6.1	Branched System	80&lt;br /&gt;
* 5.6.2	Looped System	81&lt;br /&gt;
* 5.7	Pipe network analysis	82&lt;br /&gt;
* 5.7.1	Network analysis by Conventional method (Hardy Cross)	82&lt;br /&gt;
* 5.7.2	Network Analysis by Computer Software	82&lt;br /&gt;
* 5.7.2.1	EPANET Software	82&lt;br /&gt;
* 5.7.3	Pipeline design criteria	85&lt;br /&gt;
* 5.8	Pipeline materials selection	86&lt;br /&gt;
* 5.8.1	Considerations in Selecting Pipeline Materials	86&lt;br /&gt;
* 5.8.1.1	Flow Characteristics	86&lt;br /&gt;
* 5.8.1.2	Pipe Strength	86&lt;br /&gt;
* 5.8.1.3	Durability	87&lt;br /&gt;
* 5.8.1.4	Type of Soil	87&lt;br /&gt;
* 5.8.1.5	Availability	87&lt;br /&gt;
* 5.8.1.6	Cost of Pipes	87&lt;br /&gt;
* 5.8.2	Types of Pipe Materials Available	87&lt;br /&gt;
* 5.8.2.1	Galvanized Iron (GI) Pipes	87&lt;br /&gt;
* 5.8.2.2	Plastic Pipes	87&lt;br /&gt;
* 5.9	Appurtenances for transmission and distribution mains	88&lt;br /&gt;
* 5.9.1	Valves	89&lt;br /&gt;
* 5.9.1.1	Isolation Valves	89&lt;br /&gt;
* 5.9.1.2	Check Valves	89&lt;br /&gt;
* 5.9.1.3	Float Valves	89&lt;br /&gt;
* 5.9.1.4	Air Release Valves	89&lt;br /&gt;
* 5.9.1.5	Pressure Reducing Valves	89&lt;br /&gt;
* 5.9.1.6	Washout valves	89&lt;br /&gt;
* 5.9.2	Fittings	89&lt;br /&gt;
* 5.10	References	90&lt;br /&gt;
* CHAPTER SIX	91&lt;br /&gt;
* PUMPING SYSTEMS	91&lt;br /&gt;
* 6.1	Introduction	91&lt;br /&gt;
* 6.2	Rationale	91&lt;br /&gt;
* 6.3	Common Types of Pumps used in water supply	91&lt;br /&gt;
* 6.4	Pumping System Setup	91&lt;br /&gt;
* 6.5	Source of Pumping Power	92&lt;br /&gt;
* 6.6	Pumping system design pump selection	92&lt;br /&gt;
* 6.7	Pump Protection	95&lt;br /&gt;
* 6.8	References	95&lt;br /&gt;
* CHAPTER SEVEN	96&lt;br /&gt;
* WATER TREATMENT	96&lt;br /&gt;
* 7.1	Introduction	96&lt;br /&gt;
* 7.1.1	Classification of the qualities of water sources found in Tanzania according to the complexity of its treatment	96&lt;br /&gt;
* 7.1.2	Classification of Unit Operations to achieve water treatment levels	99&lt;br /&gt;
* 7.2	Recommended overall design approach for treatment plant components	99&lt;br /&gt;
* 7.3	Documents and websites consulted and those which are hyper-linked to the DCOM Manual	100&lt;br /&gt;
* 7.4	Water treatment design considerations	100&lt;br /&gt;
* 7.5	Water treatment levels and units	101&lt;br /&gt;
* 7.5.1	Pre-treatment	101&lt;br /&gt;
* 7.5.1.1	Scum and Floating Materials Skimmer	101&lt;br /&gt;
* 7.5.1.2	Screening or straining	101&lt;br /&gt;
* 7.5.1.3	Grit Removal	103&lt;br /&gt;
* 7.5.1.3.1	Design criteria	103&lt;br /&gt;
* 7.5.1.4	Sand Traps	105&lt;br /&gt;
* 7.5.1.5	Pre-chlorination	107&lt;br /&gt;
* 7.5.1.6	Water pre-conditioning (pH adjustment)	108&lt;br /&gt;
* 7.5.2	Primary Treatment	108&lt;br /&gt;
* 7.5.2.1	Sedimentation	108&lt;br /&gt;
* 7.5.2.2	Primary Filtration	114&lt;br /&gt;
* 7.5.2.2.1	Slow Sand Filtration	114&lt;br /&gt;
* 7.5.2.2.2	Rapid Gravity Sand Filtration	117&lt;br /&gt;
* 7.5.2.2.3	Comparison between Slow Sand Filters and Rapid Sand Filters	118&lt;br /&gt;
* 7.5.2.2.4	Other Types of Filters	119&lt;br /&gt;
* 7.5.2.3	Floatation	124&lt;br /&gt;
* 7.5.2.3.1	Dissolved-Air Floatation	124&lt;br /&gt;
* 7.5.2.3.2	Electrolytic Floatation	125&lt;br /&gt;
* 7.5.2.3.3	Dispersed-Air Floatation	125&lt;br /&gt;
* 7.5.2.4	Aeration	125&lt;br /&gt;
* 7.5.2.4.1	Falling Water Aerators	126&lt;br /&gt;
* 7.5.2.4.2	Spray Aerators	127&lt;br /&gt;
* 7.5.3	Secondary Treatment	130&lt;br /&gt;
* 7.5.3.1	Clarification	130&lt;br /&gt;
* 7.5.3.2	Coagulation	130&lt;br /&gt;
* 7.5.3.3	Flocculation	131&lt;br /&gt;
* 7.5.3.4	Filtration	131&lt;br /&gt;
* 7.5.4	Tertiary Treatment	132&lt;br /&gt;
* 7.5.4.1	Disinfection	132&lt;br /&gt;
* 7.5.4.1.1	Disinfection Methods	132&lt;br /&gt;
* 7.5.4.1.2	Chlorinators	132&lt;br /&gt;
* 7.5.4.1.3	Design considerations for chlorinators	133&lt;br /&gt;
* 7.5.4.2	Ozonation	133&lt;br /&gt;
* 7.5.4.3	Water softening	134&lt;br /&gt;
* 7.5.4.3.1	Methods of Softening	135&lt;br /&gt;
* 7.5.4.4	Defluoridation of Water	139&lt;br /&gt;
* 7.5.4.4.1	Fluorides	139&lt;br /&gt;
* 7.5.4.4.2	Defluoridation	139&lt;br /&gt;
* 7.5.4.5	Water Conditioning	141&lt;br /&gt;
* 7.5.5	Managemen&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=493</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=493"/>
		<updated>2020-03-30T19:03:54Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[Chapter_One:_Introduction|CHAPTER ONE: INTRODUCTION]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[CHAPTER TWO: PROJECT PLANNING|CHAPTER TWO: PROJECT PLANNING]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[CHAPTER THREE: WATER SOURCES ANALYSIS|CHAPTER THREE: WATER SOURCES ANALYSIS]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[CHAPTER FOUR: WATER DEMAND ASSESSMENT|CHAPTER FOUR: WATER DEMAND ASSESSMENT]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[CHAPTER FIVE: PIPELINES DESIGN|CHAPTER FIVE: PIPELINES DESIGN]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[CHAPTER SIX: PUMPING SYSTEMS|CHAPTER SIX: PUMPING SYSTEMS]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[CHAPTER SEVEN: WATER TREATMENT|CHAPTER SEVEN: WATER TREATMENT]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[CHAPTER EIGHT: TREATMENT OF WATERS WITH SPECIAL CONTAMINANTS|CHAPTER EIGHT: TREATMENT OF WATERS WITH SPECIAL CONTAMINANTS]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[CHAPTER NINE: DESIGN OF WATER STRUCTURES|CHAPTER NINE: DESIGN OF WATER STRUCTURES]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[CHAPTER TEN: APPLICATION SOFTWARE|CHAPTER TEN: APPLICATION SOFTWARE]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[CHAPTER ELEVEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[CHAPTER TWELVE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[CHAPTER THIRTEEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[APENDICES: APPENDICES]] || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Chapter #!! Chapter Title!! Page&lt;br /&gt;
|-&lt;br /&gt;
| i || LIST OF SPECIAL COMMITTEE MEMBERS || V&lt;br /&gt;
|-&lt;br /&gt;
| 1|| CHAPTER ONE: INTRODUCTION		 || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1|| Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.1 || Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.2 || Climate Change and Resilience to Climate Change || 2&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.3 || Public-Private Partnership in Water Supply and Sanitation Projects in Developing Countries || 3&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.4 || International Water Law || 4&lt;br /&gt;
|-&lt;br /&gt;
| 1.2 || Development Agenda and Water and Sanitation Sector in Tanzania || 5&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.1 || National Water Policy || 7&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.2|| Legal and Institutional Framework for Water Supply and Sanitation Services || 8&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.3 || Coverage and Access to Water Supply Services || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.4|| Policy Environment for Water and Sanitation Services in Tanzania || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.5 || Major Stakeholders in  Water Supply and Sanitation Projects || 10&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.6 || Water Supply and Sanitation Public Private Partnership in Tanzania || 11&lt;br /&gt;
|-&lt;br /&gt;
| 1.3 || Rationale for Preparation of the Fourth Edition DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.4 || About the Fourth Edition of the DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.5 || Organisation of the 4th edition of the DCOM Manual || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.6 || Purpose of this Volume || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.7 || References	 || 15&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
* CHAPTER TWO	17&lt;br /&gt;
* PROJECT PLANNING	17&lt;br /&gt;
* 2.1	Planning Considerations for Water Supply Projects	17&lt;br /&gt;
* 2.2	Project Planning Steps	18&lt;br /&gt;
* 2.3	Pump Protection	18&lt;br /&gt;
* 2.3.1	Initiation	18&lt;br /&gt;
* 2.3.1.1	Community Assessment Steps	20&lt;br /&gt;
* 2.3.1.2	Methods of conducting community assessment	20&lt;br /&gt;
* 2.3.1.2.1	Comprehensive community assessment	20&lt;br /&gt;
* 2.3.1.2.2	Strategic community assessment	20&lt;br /&gt;
* 2.3.2	Pre-feasibility Study	21&lt;br /&gt;
* 2.3.3	Feasibility Study	21&lt;br /&gt;
* 2.3.3.1	Water Supply Projects Ranking and Technology Selection Criteria	22&lt;br /&gt;
* 2.3.3.1.1	Ranking of Projects	22&lt;br /&gt;
* 2.3.3.1.2	Choice of Technology	23&lt;br /&gt;
* 2.3.4	Preliminary and Detailed Design	23&lt;br /&gt;
* 2.3.4.1	Detailed Engineering Drawings	24&lt;br /&gt;
* 2.3.4.2	Detailed estimates of capital costs	24&lt;br /&gt;
* 2.3.4.3	Detailed estimates of recurrent costs	24&lt;br /&gt;
* 2.3.4.4	Anticipated revenue	25&lt;br /&gt;
* 2.3.4.5	Detailed design report	25&lt;br /&gt;
* 2.3.4.6	Project write-up to be submitted to potential financiers	25&lt;br /&gt;
* 2.3.5	Project Phasing	25&lt;br /&gt;
* 2.3.6	Procurement	26&lt;br /&gt;
* 2.3.6.1	2.2.6.1 Preparation of Tender Documents	26&lt;br /&gt;
* 2.3.6.2	Tendering process	27&lt;br /&gt;
* 2.3.7	Implementation/Construction Stage	27&lt;br /&gt;
* 2.3.7.1	Contract Management	27&lt;br /&gt;
* 2.3.7.2	Contract supervision and administration	27&lt;br /&gt;
* 2.3.8	Operation and Maintenance Stage	28&lt;br /&gt;
* 2.3.9	Performance Monitoring	28&lt;br /&gt;
* 2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans	28&lt;br /&gt;
* 2.4.1	Status of Development and Implementation of IWRMD Plans	29&lt;br /&gt;
* 2.4.2	Components of IWRMD Plans	30&lt;br /&gt;
* 2.5	Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change	30&lt;br /&gt;
* 2.6	Environmental and Social Impact Assessment Compliance	30&lt;br /&gt;
* 2.6.1	Procedures for Conducting ESIA in Tanzania	31&lt;br /&gt;
* 2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance	31&lt;br /&gt;
* 2.7	Potential Impacts of Climate Change on Water Supply Projects	32&lt;br /&gt;
* 2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages	32&lt;br /&gt;
* 2.9	References	32&lt;br /&gt;
* CHAPTER THREE	35&lt;br /&gt;
* WATER SOURCES ANALYSIS	35&lt;br /&gt;
* 3.1	Availability of Water Resources in Tanzania Mainland	35&lt;br /&gt;
* 3.2	Water Sources Available in Tanzania Mainland	38&lt;br /&gt;
* 3.2.1	Rainwater and fog harvesting	39&lt;br /&gt;
* 3.2.2	Surface Water	39&lt;br /&gt;
* 3.2.2.1	Rivers or streams	39&lt;br /&gt;
* 3.2.2.2	Impoundments	39&lt;br /&gt;
* 3.2.2.3	Springs	39&lt;br /&gt;
* 3.2.2.4	Lakes	39&lt;br /&gt;
* 3.2.2.5	Dams	40&lt;br /&gt;
* 3.2.3	Groundwater	40&lt;br /&gt;
* 3.2.3.1	Infiltration galleries/wells	40&lt;br /&gt;
* 3.2.3.2	Well	40&lt;br /&gt;
* 3.2.3.3	Classification of wells based on the aquifer tapped	41&lt;br /&gt;
* 3.2.3.3.1	Shallow wells	41&lt;br /&gt;
* 3.2.3.3.2	Deep wells	41&lt;br /&gt;
* 3.2.3.3.3	Artesian wells	41&lt;br /&gt;
* 3.3	Quality Suitability of Water Sources for Water Supply Projects	42&lt;br /&gt;
* 3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment	42&lt;br /&gt;
* 3.5	General Considerations for Selection of Water Sources	42&lt;br /&gt;
* 3.5.1	Adequacy and reliability	42&lt;br /&gt;
* 3.5.2	Quality of water sources	43&lt;br /&gt;
* 3.5.3	Technical Requirements	43&lt;br /&gt;
* 3.5.4	Cost implications to develop a water source	43&lt;br /&gt;
* 3.5.5	Protection of water sources	43&lt;br /&gt;
* 3.5.6	Legal and management requirements	44&lt;br /&gt;
* 3.5.7	Distance of water supply source	44&lt;br /&gt;
* 3.5.8	Topography of the project area and its surroundings	44&lt;br /&gt;
* 3.5.9	Elevation of a source of water supply	44&lt;br /&gt;
* 3.6	Determination of water source yield	44&lt;br /&gt;
* 3.6.1	Rainwater and fog harvesting	45&lt;br /&gt;
* 3.6.1.1	Rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.1	Types of rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.2	Components of rainwater harvesting system	46&lt;br /&gt;
* 3.6.1.1.3	Estimation of the yield	47&lt;br /&gt;
* 3.6.2	Hydrological Analysis of Surface Waters	47&lt;br /&gt;
* 3.7	Other considerations for various water sources	55&lt;br /&gt;
* 3.7.1	Water permits Considerations	55&lt;br /&gt;
* 3.7.2	Conservation of water sources	55&lt;br /&gt;
* 3.8	References	55&lt;br /&gt;
* CHAPTER FOUR	56&lt;br /&gt;
* WATER DEMAND ASSESSMENT	56&lt;br /&gt;
* 4.1	Water Demand Assessment	56&lt;br /&gt;
* 4.2	General Factors Affecting Water Demand Assessment	57&lt;br /&gt;
* 4.3	Determination of Water Demand for Different Uses	58&lt;br /&gt;
* Step 7. Establish Net Water Demand	67&lt;br /&gt;
* Step 9: Establish Operational water consumption	67&lt;br /&gt;
* Step 10: Establish System water losses	68&lt;br /&gt;
* Step 11 Establish Non-Revenue Water	69&lt;br /&gt;
* 4.4	Variations in Water Consumption	70&lt;br /&gt;
* 4.4.1	Definitions	70&lt;br /&gt;
* 4.4.2	Variation in the Rate of Consumption	71&lt;br /&gt;
* 4.4.2.1	Diurnal variation in demand	71&lt;br /&gt;
* 4.4.3	Peak Factors	72&lt;br /&gt;
* 4.4.4	Predicting Demand	74&lt;br /&gt;
* 4.4.5	Design Demand	75&lt;br /&gt;
* 4.5	References	75&lt;br /&gt;
* CHAPTER FIVE	76&lt;br /&gt;
* PIPELINES DESIGN	76&lt;br /&gt;
* 5.1	Design Requirements of pipelines	76&lt;br /&gt;
* 5.2	Types of pipelines	76&lt;br /&gt;
* 5.3	Security considerations for pipelines	76&lt;br /&gt;
* 5.3.1	Methods of water transmission and distribution	76&lt;br /&gt;
* 5.3.2	Gravity flow	77&lt;br /&gt;
* 5.3.3	Pumping with storage	77&lt;br /&gt;
* 5.3.4	Direct pumping to the distribution system	77&lt;br /&gt;
* 5.4	Pipeline Hydraulics Assessment	77&lt;br /&gt;
* 5.4.1	Pressure	77&lt;br /&gt;
* 5.4.2	Determination of Head Losses	77&lt;br /&gt;
* 5.5	Water supply transmission system	79&lt;br /&gt;
* 5.5.1	Determination of Transmission Pipe Size	79&lt;br /&gt;
* 5.5.2	Maximum Pressure	79&lt;br /&gt;
* 5.6	Distribution system	80&lt;br /&gt;
* 5.6.1	Branched System	80&lt;br /&gt;
* 5.6.2	Looped System	81&lt;br /&gt;
* 5.7	Pipe network analysis	82&lt;br /&gt;
* 5.7.1	Network analysis by Conventional method (Hardy Cross)	82&lt;br /&gt;
* 5.7.2	Network Analysis by Computer Software	82&lt;br /&gt;
* 5.7.2.1	EPANET Software	82&lt;br /&gt;
* 5.7.3	Pipeline design criteria	85&lt;br /&gt;
* 5.8	Pipeline materials selection	86&lt;br /&gt;
* 5.8.1	Considerations in Selecting Pipeline Materials	86&lt;br /&gt;
* 5.8.1.1	Flow Characteristics	86&lt;br /&gt;
* 5.8.1.2	Pipe Strength	86&lt;br /&gt;
* 5.8.1.3	Durability	87&lt;br /&gt;
* 5.8.1.4	Type of Soil	87&lt;br /&gt;
* 5.8.1.5	Availability	87&lt;br /&gt;
* 5.8.1.6	Cost of Pipes	87&lt;br /&gt;
* 5.8.2	Types of Pipe Materials Available	87&lt;br /&gt;
* 5.8.2.1	Galvanized Iron (GI) Pipes	87&lt;br /&gt;
* 5.8.2.2	Plastic Pipes	87&lt;br /&gt;
* 5.9	Appurtenances for transmission and distribution mains	88&lt;br /&gt;
* 5.9.1	Valves	89&lt;br /&gt;
* 5.9.1.1	Isolation Valves	89&lt;br /&gt;
* 5.9.1.2	Check Valves	89&lt;br /&gt;
* 5.9.1.3	Float Valves	89&lt;br /&gt;
* 5.9.1.4	Air Release Valves	89&lt;br /&gt;
* 5.9.1.5	Pressure Reducing Valves	89&lt;br /&gt;
* 5.9.1.6	Washout valves	89&lt;br /&gt;
* 5.9.2	Fittings	89&lt;br /&gt;
* 5.10	References	90&lt;br /&gt;
* CHAPTER SIX	91&lt;br /&gt;
* PUMPING SYSTEMS	91&lt;br /&gt;
* 6.1	Introduction	91&lt;br /&gt;
* 6.2	Rationale	91&lt;br /&gt;
* 6.3	Common Types of Pumps used in water supply	91&lt;br /&gt;
* 6.4	Pumping System Setup	91&lt;br /&gt;
* 6.5	Source of Pumping Power	92&lt;br /&gt;
* 6.6	Pumping system design pump selection	92&lt;br /&gt;
* 6.7	Pump Protection	95&lt;br /&gt;
* 6.8	References	95&lt;br /&gt;
* CHAPTER SEVEN	96&lt;br /&gt;
* WATER TREATMENT	96&lt;br /&gt;
* 7.1	Introduction	96&lt;br /&gt;
* 7.1.1	Classification of the qualities of water sources found in Tanzania according to the complexity of its treatment	96&lt;br /&gt;
* 7.1.2	Classification of Unit Operations to achieve water treatment levels	99&lt;br /&gt;
* 7.2	Recommended overall design approach for treatment plant components	99&lt;br /&gt;
* 7.3	Documents and websites consulted and those which are hyper-linked to the DCOM Manual	100&lt;br /&gt;
* 7.4	Water treatment design considerations	100&lt;br /&gt;
* 7.5	Water treatment levels and units	101&lt;br /&gt;
* 7.5.1	Pre-treatment	101&lt;br /&gt;
* 7.5.1.1	Scum and Floating Materials Skimmer	101&lt;br /&gt;
* 7.5.1.2	Screening or straining	101&lt;br /&gt;
* 7.5.1.3	Grit Removal	103&lt;br /&gt;
* 7.5.1.3.1	Design criteria	103&lt;br /&gt;
* 7.5.1.4	Sand Traps	105&lt;br /&gt;
* 7.5.1.5	Pre-chlorination	107&lt;br /&gt;
* 7.5.1.6	Water pre-conditioning (pH adjustment)	108&lt;br /&gt;
* 7.5.2	Primary Treatment	108&lt;br /&gt;
* 7.5.2.1	Sedimentation	108&lt;br /&gt;
* 7.5.2.2	Primary Filtration	114&lt;br /&gt;
* 7.5.2.2.1	Slow Sand Filtration	114&lt;br /&gt;
* 7.5.2.2.2	Rapid Gravity Sand Filtration	117&lt;br /&gt;
* 7.5.2.2.3	Comparison between Slow Sand Filters and Rapid Sand Filters	118&lt;br /&gt;
* 7.5.2.2.4	Other Types of Filters	119&lt;br /&gt;
* 7.5.2.3	Floatation	124&lt;br /&gt;
* 7.5.2.3.1	Dissolved-Air Floatation	124&lt;br /&gt;
* 7.5.2.3.2	Electrolytic Floatation	125&lt;br /&gt;
* 7.5.2.3.3	Dispersed-Air Floatation	125&lt;br /&gt;
* 7.5.2.4	Aeration	125&lt;br /&gt;
* 7.5.2.4.1	Falling Water Aerators	126&lt;br /&gt;
* 7.5.2.4.2	Spray Aerators	127&lt;br /&gt;
* 7.5.3	Secondary Treatment	130&lt;br /&gt;
* 7.5.3.1	Clarification	130&lt;br /&gt;
* 7.5.3.2	Coagulation	130&lt;br /&gt;
* 7.5.3.3	Flocculation	131&lt;br /&gt;
* 7.5.3.4	Filtration	131&lt;br /&gt;
* 7.5.4	Tertiary Treatment	132&lt;br /&gt;
* 7.5.4.1	Disinfection	132&lt;br /&gt;
* 7.5.4.1.1	Disinfection Methods	132&lt;br /&gt;
* 7.5.4.1.2	Chlorinators	132&lt;br /&gt;
* 7.5.4.1.3	Design considerations for chlorinators	133&lt;br /&gt;
* 7.5.4.2	Ozonation	133&lt;br /&gt;
* 7.5.4.3	Water softening	134&lt;br /&gt;
* 7.5.4.3.1	Methods of Softening	135&lt;br /&gt;
* 7.5.4.4	Defluoridation of Water	139&lt;br /&gt;
* 7.5.4.4.1	Fluorides	139&lt;br /&gt;
* 7.5.4.4.2	Defluoridation	139&lt;br /&gt;
* 7.5.4.5	Water Conditioning	141&lt;br /&gt;
* 7.5.5	Managemen&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=492</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=492"/>
		<updated>2020-03-30T19:02:37Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[CHAPTER ONE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[CHAPTER TWO: PROJECT PLANNING|CHAPTER TWO: PROJECT PLANNING]] || 17&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[CHAPTER THREE: WATER SOURCES ANALYSIS|CHAPTER THREE: WATER SOURCES ANALYSIS]] || 35&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[CHAPTER FOUR: WATER DEMAND ASSESSMENT|CHAPTER FOUR: WATER DEMAND ASSESSMENT]] || 56&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[CHAPTER FIVE: PIPELINES DESIGN|CHAPTER FIVE: PIPELINES DESIGN]] || 76&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[CHAPTER SIX: PUMPING SYSTEMS|CHAPTER SIX: PUMPING SYSTEMS]] || 91&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[CHAPTER SEVEN: WATER TREATMENT|CHAPTER SEVEN: WATER TREATMENT]] || 96&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[CHAPTER EIGHT: TREATMENT OF WATERS WITH SPECIAL CONTAMINANTS|CHAPTER EIGHT: TREATMENT OF WATERS WITH SPECIAL CONTAMINANTS]] || 148&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[CHAPTER NINE: DESIGN OF WATER STRUCTURES|CHAPTER NINE: DESIGN OF WATER STRUCTURES]] || 159&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[CHAPTER TEN: APPLICATION SOFTWARE|CHAPTER TEN: APPLICATION SOFTWARE]] || 203&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[CHAPTER ELEVEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[CHAPTER TWELVE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[CHAPTER THIRTEEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[APENDICES: APPENDICES]] || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Chapter #!! Chapter Title!! Page&lt;br /&gt;
|-&lt;br /&gt;
| i || LIST OF SPECIAL COMMITTEE MEMBERS || V&lt;br /&gt;
|-&lt;br /&gt;
| 1|| CHAPTER ONE: INTRODUCTION		 || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1|| Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.1 || Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.2 || Climate Change and Resilience to Climate Change || 2&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.3 || Public-Private Partnership in Water Supply and Sanitation Projects in Developing Countries || 3&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.4 || International Water Law || 4&lt;br /&gt;
|-&lt;br /&gt;
| 1.2 || Development Agenda and Water and Sanitation Sector in Tanzania || 5&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.1 || National Water Policy || 7&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.2|| Legal and Institutional Framework for Water Supply and Sanitation Services || 8&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.3 || Coverage and Access to Water Supply Services || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.4|| Policy Environment for Water and Sanitation Services in Tanzania || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.5 || Major Stakeholders in  Water Supply and Sanitation Projects || 10&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.6 || Water Supply and Sanitation Public Private Partnership in Tanzania || 11&lt;br /&gt;
|-&lt;br /&gt;
| 1.3 || Rationale for Preparation of the Fourth Edition DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.4 || About the Fourth Edition of the DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.5 || Organisation of the 4th edition of the DCOM Manual || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.6 || Purpose of this Volume || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.7 || References	 || 15&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
* CHAPTER TWO	17&lt;br /&gt;
* PROJECT PLANNING	17&lt;br /&gt;
* 2.1	Planning Considerations for Water Supply Projects	17&lt;br /&gt;
* 2.2	Project Planning Steps	18&lt;br /&gt;
* 2.3	Pump Protection	18&lt;br /&gt;
* 2.3.1	Initiation	18&lt;br /&gt;
* 2.3.1.1	Community Assessment Steps	20&lt;br /&gt;
* 2.3.1.2	Methods of conducting community assessment	20&lt;br /&gt;
* 2.3.1.2.1	Comprehensive community assessment	20&lt;br /&gt;
* 2.3.1.2.2	Strategic community assessment	20&lt;br /&gt;
* 2.3.2	Pre-feasibility Study	21&lt;br /&gt;
* 2.3.3	Feasibility Study	21&lt;br /&gt;
* 2.3.3.1	Water Supply Projects Ranking and Technology Selection Criteria	22&lt;br /&gt;
* 2.3.3.1.1	Ranking of Projects	22&lt;br /&gt;
* 2.3.3.1.2	Choice of Technology	23&lt;br /&gt;
* 2.3.4	Preliminary and Detailed Design	23&lt;br /&gt;
* 2.3.4.1	Detailed Engineering Drawings	24&lt;br /&gt;
* 2.3.4.2	Detailed estimates of capital costs	24&lt;br /&gt;
* 2.3.4.3	Detailed estimates of recurrent costs	24&lt;br /&gt;
* 2.3.4.4	Anticipated revenue	25&lt;br /&gt;
* 2.3.4.5	Detailed design report	25&lt;br /&gt;
* 2.3.4.6	Project write-up to be submitted to potential financiers	25&lt;br /&gt;
* 2.3.5	Project Phasing	25&lt;br /&gt;
* 2.3.6	Procurement	26&lt;br /&gt;
* 2.3.6.1	2.2.6.1 Preparation of Tender Documents	26&lt;br /&gt;
* 2.3.6.2	Tendering process	27&lt;br /&gt;
* 2.3.7	Implementation/Construction Stage	27&lt;br /&gt;
* 2.3.7.1	Contract Management	27&lt;br /&gt;
* 2.3.7.2	Contract supervision and administration	27&lt;br /&gt;
* 2.3.8	Operation and Maintenance Stage	28&lt;br /&gt;
* 2.3.9	Performance Monitoring	28&lt;br /&gt;
* 2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans	28&lt;br /&gt;
* 2.4.1	Status of Development and Implementation of IWRMD Plans	29&lt;br /&gt;
* 2.4.2	Components of IWRMD Plans	30&lt;br /&gt;
* 2.5	Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change	30&lt;br /&gt;
* 2.6	Environmental and Social Impact Assessment Compliance	30&lt;br /&gt;
* 2.6.1	Procedures for Conducting ESIA in Tanzania	31&lt;br /&gt;
* 2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance	31&lt;br /&gt;
* 2.7	Potential Impacts of Climate Change on Water Supply Projects	32&lt;br /&gt;
* 2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages	32&lt;br /&gt;
* 2.9	References	32&lt;br /&gt;
* CHAPTER THREE	35&lt;br /&gt;
* WATER SOURCES ANALYSIS	35&lt;br /&gt;
* 3.1	Availability of Water Resources in Tanzania Mainland	35&lt;br /&gt;
* 3.2	Water Sources Available in Tanzania Mainland	38&lt;br /&gt;
* 3.2.1	Rainwater and fog harvesting	39&lt;br /&gt;
* 3.2.2	Surface Water	39&lt;br /&gt;
* 3.2.2.1	Rivers or streams	39&lt;br /&gt;
* 3.2.2.2	Impoundments	39&lt;br /&gt;
* 3.2.2.3	Springs	39&lt;br /&gt;
* 3.2.2.4	Lakes	39&lt;br /&gt;
* 3.2.2.5	Dams	40&lt;br /&gt;
* 3.2.3	Groundwater	40&lt;br /&gt;
* 3.2.3.1	Infiltration galleries/wells	40&lt;br /&gt;
* 3.2.3.2	Well	40&lt;br /&gt;
* 3.2.3.3	Classification of wells based on the aquifer tapped	41&lt;br /&gt;
* 3.2.3.3.1	Shallow wells	41&lt;br /&gt;
* 3.2.3.3.2	Deep wells	41&lt;br /&gt;
* 3.2.3.3.3	Artesian wells	41&lt;br /&gt;
* 3.3	Quality Suitability of Water Sources for Water Supply Projects	42&lt;br /&gt;
* 3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment	42&lt;br /&gt;
* 3.5	General Considerations for Selection of Water Sources	42&lt;br /&gt;
* 3.5.1	Adequacy and reliability	42&lt;br /&gt;
* 3.5.2	Quality of water sources	43&lt;br /&gt;
* 3.5.3	Technical Requirements	43&lt;br /&gt;
* 3.5.4	Cost implications to develop a water source	43&lt;br /&gt;
* 3.5.5	Protection of water sources	43&lt;br /&gt;
* 3.5.6	Legal and management requirements	44&lt;br /&gt;
* 3.5.7	Distance of water supply source	44&lt;br /&gt;
* 3.5.8	Topography of the project area and its surroundings	44&lt;br /&gt;
* 3.5.9	Elevation of a source of water supply	44&lt;br /&gt;
* 3.6	Determination of water source yield	44&lt;br /&gt;
* 3.6.1	Rainwater and fog harvesting	45&lt;br /&gt;
* 3.6.1.1	Rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.1	Types of rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.2	Components of rainwater harvesting system	46&lt;br /&gt;
* 3.6.1.1.3	Estimation of the yield	47&lt;br /&gt;
* 3.6.2	Hydrological Analysis of Surface Waters	47&lt;br /&gt;
* 3.7	Other considerations for various water sources	55&lt;br /&gt;
* 3.7.1	Water permits Considerations	55&lt;br /&gt;
* 3.7.2	Conservation of water sources	55&lt;br /&gt;
* 3.8	References	55&lt;br /&gt;
* CHAPTER FOUR	56&lt;br /&gt;
* WATER DEMAND ASSESSMENT	56&lt;br /&gt;
* 4.1	Water Demand Assessment	56&lt;br /&gt;
* 4.2	General Factors Affecting Water Demand Assessment	57&lt;br /&gt;
* 4.3	Determination of Water Demand for Different Uses	58&lt;br /&gt;
* Step 7. Establish Net Water Demand	67&lt;br /&gt;
* Step 9: Establish Operational water consumption	67&lt;br /&gt;
* Step 10: Establish System water losses	68&lt;br /&gt;
* Step 11 Establish Non-Revenue Water	69&lt;br /&gt;
* 4.4	Variations in Water Consumption	70&lt;br /&gt;
* 4.4.1	Definitions	70&lt;br /&gt;
* 4.4.2	Variation in the Rate of Consumption	71&lt;br /&gt;
* 4.4.2.1	Diurnal variation in demand	71&lt;br /&gt;
* 4.4.3	Peak Factors	72&lt;br /&gt;
* 4.4.4	Predicting Demand	74&lt;br /&gt;
* 4.4.5	Design Demand	75&lt;br /&gt;
* 4.5	References	75&lt;br /&gt;
* CHAPTER FIVE	76&lt;br /&gt;
* PIPELINES DESIGN	76&lt;br /&gt;
* 5.1	Design Requirements of pipelines	76&lt;br /&gt;
* 5.2	Types of pipelines	76&lt;br /&gt;
* 5.3	Security considerations for pipelines	76&lt;br /&gt;
* 5.3.1	Methods of water transmission and distribution	76&lt;br /&gt;
* 5.3.2	Gravity flow	77&lt;br /&gt;
* 5.3.3	Pumping with storage	77&lt;br /&gt;
* 5.3.4	Direct pumping to the distribution system	77&lt;br /&gt;
* 5.4	Pipeline Hydraulics Assessment	77&lt;br /&gt;
* 5.4.1	Pressure	77&lt;br /&gt;
* 5.4.2	Determination of Head Losses	77&lt;br /&gt;
* 5.5	Water supply transmission system	79&lt;br /&gt;
* 5.5.1	Determination of Transmission Pipe Size	79&lt;br /&gt;
* 5.5.2	Maximum Pressure	79&lt;br /&gt;
* 5.6	Distribution system	80&lt;br /&gt;
* 5.6.1	Branched System	80&lt;br /&gt;
* 5.6.2	Looped System	81&lt;br /&gt;
* 5.7	Pipe network analysis	82&lt;br /&gt;
* 5.7.1	Network analysis by Conventional method (Hardy Cross)	82&lt;br /&gt;
* 5.7.2	Network Analysis by Computer Software	82&lt;br /&gt;
* 5.7.2.1	EPANET Software	82&lt;br /&gt;
* 5.7.3	Pipeline design criteria	85&lt;br /&gt;
* 5.8	Pipeline materials selection	86&lt;br /&gt;
* 5.8.1	Considerations in Selecting Pipeline Materials	86&lt;br /&gt;
* 5.8.1.1	Flow Characteristics	86&lt;br /&gt;
* 5.8.1.2	Pipe Strength	86&lt;br /&gt;
* 5.8.1.3	Durability	87&lt;br /&gt;
* 5.8.1.4	Type of Soil	87&lt;br /&gt;
* 5.8.1.5	Availability	87&lt;br /&gt;
* 5.8.1.6	Cost of Pipes	87&lt;br /&gt;
* 5.8.2	Types of Pipe Materials Available	87&lt;br /&gt;
* 5.8.2.1	Galvanized Iron (GI) Pipes	87&lt;br /&gt;
* 5.8.2.2	Plastic Pipes	87&lt;br /&gt;
* 5.9	Appurtenances for transmission and distribution mains	88&lt;br /&gt;
* 5.9.1	Valves	89&lt;br /&gt;
* 5.9.1.1	Isolation Valves	89&lt;br /&gt;
* 5.9.1.2	Check Valves	89&lt;br /&gt;
* 5.9.1.3	Float Valves	89&lt;br /&gt;
* 5.9.1.4	Air Release Valves	89&lt;br /&gt;
* 5.9.1.5	Pressure Reducing Valves	89&lt;br /&gt;
* 5.9.1.6	Washout valves	89&lt;br /&gt;
* 5.9.2	Fittings	89&lt;br /&gt;
* 5.10	References	90&lt;br /&gt;
* CHAPTER SIX	91&lt;br /&gt;
* PUMPING SYSTEMS	91&lt;br /&gt;
* 6.1	Introduction	91&lt;br /&gt;
* 6.2	Rationale	91&lt;br /&gt;
* 6.3	Common Types of Pumps used in water supply	91&lt;br /&gt;
* 6.4	Pumping System Setup	91&lt;br /&gt;
* 6.5	Source of Pumping Power	92&lt;br /&gt;
* 6.6	Pumping system design pump selection	92&lt;br /&gt;
* 6.7	Pump Protection	95&lt;br /&gt;
* 6.8	References	95&lt;br /&gt;
* CHAPTER SEVEN	96&lt;br /&gt;
* WATER TREATMENT	96&lt;br /&gt;
* 7.1	Introduction	96&lt;br /&gt;
* 7.1.1	Classification of the qualities of water sources found in Tanzania according to the complexity of its treatment	96&lt;br /&gt;
* 7.1.2	Classification of Unit Operations to achieve water treatment levels	99&lt;br /&gt;
* 7.2	Recommended overall design approach for treatment plant components	99&lt;br /&gt;
* 7.3	Documents and websites consulted and those which are hyper-linked to the DCOM Manual	100&lt;br /&gt;
* 7.4	Water treatment design considerations	100&lt;br /&gt;
* 7.5	Water treatment levels and units	101&lt;br /&gt;
* 7.5.1	Pre-treatment	101&lt;br /&gt;
* 7.5.1.1	Scum and Floating Materials Skimmer	101&lt;br /&gt;
* 7.5.1.2	Screening or straining	101&lt;br /&gt;
* 7.5.1.3	Grit Removal	103&lt;br /&gt;
* 7.5.1.3.1	Design criteria	103&lt;br /&gt;
* 7.5.1.4	Sand Traps	105&lt;br /&gt;
* 7.5.1.5	Pre-chlorination	107&lt;br /&gt;
* 7.5.1.6	Water pre-conditioning (pH adjustment)	108&lt;br /&gt;
* 7.5.2	Primary Treatment	108&lt;br /&gt;
* 7.5.2.1	Sedimentation	108&lt;br /&gt;
* 7.5.2.2	Primary Filtration	114&lt;br /&gt;
* 7.5.2.2.1	Slow Sand Filtration	114&lt;br /&gt;
* 7.5.2.2.2	Rapid Gravity Sand Filtration	117&lt;br /&gt;
* 7.5.2.2.3	Comparison between Slow Sand Filters and Rapid Sand Filters	118&lt;br /&gt;
* 7.5.2.2.4	Other Types of Filters	119&lt;br /&gt;
* 7.5.2.3	Floatation	124&lt;br /&gt;
* 7.5.2.3.1	Dissolved-Air Floatation	124&lt;br /&gt;
* 7.5.2.3.2	Electrolytic Floatation	125&lt;br /&gt;
* 7.5.2.3.3	Dispersed-Air Floatation	125&lt;br /&gt;
* 7.5.2.4	Aeration	125&lt;br /&gt;
* 7.5.2.4.1	Falling Water Aerators	126&lt;br /&gt;
* 7.5.2.4.2	Spray Aerators	127&lt;br /&gt;
* 7.5.3	Secondary Treatment	130&lt;br /&gt;
* 7.5.3.1	Clarification	130&lt;br /&gt;
* 7.5.3.2	Coagulation	130&lt;br /&gt;
* 7.5.3.3	Flocculation	131&lt;br /&gt;
* 7.5.3.4	Filtration	131&lt;br /&gt;
* 7.5.4	Tertiary Treatment	132&lt;br /&gt;
* 7.5.4.1	Disinfection	132&lt;br /&gt;
* 7.5.4.1.1	Disinfection Methods	132&lt;br /&gt;
* 7.5.4.1.2	Chlorinators	132&lt;br /&gt;
* 7.5.4.1.3	Design considerations for chlorinators	133&lt;br /&gt;
* 7.5.4.2	Ozonation	133&lt;br /&gt;
* 7.5.4.3	Water softening	134&lt;br /&gt;
* 7.5.4.3.1	Methods of Softening	135&lt;br /&gt;
* 7.5.4.4	Defluoridation of Water	139&lt;br /&gt;
* 7.5.4.4.1	Fluorides	139&lt;br /&gt;
* 7.5.4.4.2	Defluoridation	139&lt;br /&gt;
* 7.5.4.5	Water Conditioning	141&lt;br /&gt;
* 7.5.5	Managemen&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=491</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=491"/>
		<updated>2020-03-30T18:53:59Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[CHAPTER ONE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[CHAPTER TWO: INTRODUCTION|CHAPTER TWO: PROJECT PLANNING]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[CHAPTER THREE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[CHAPTER FOUR: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[CHAPTER FIVE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[CHAPTER SIX: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[CHAPTER SEVEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[CHAPTER EIGHT: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[CHAPTER NINE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[CHAPTER TEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[CHAPTER ELEVEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[CHAPTER TWELVE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[CHAPTER THIRTEEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[APENDICES: APPENDICES]] || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Chapter #!! Chapter Title!! Page&lt;br /&gt;
|-&lt;br /&gt;
| i || LIST OF SPECIAL COMMITTEE MEMBERS || V&lt;br /&gt;
|-&lt;br /&gt;
| 1|| CHAPTER ONE: INTRODUCTION		 || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1|| Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.1 || Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.2 || Climate Change and Resilience to Climate Change || 2&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.3 || Public-Private Partnership in Water Supply and Sanitation Projects in Developing Countries || 3&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.4 || International Water Law || 4&lt;br /&gt;
|-&lt;br /&gt;
| 1.2 || Development Agenda and Water and Sanitation Sector in Tanzania || 5&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.1 || National Water Policy || 7&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.2|| Legal and Institutional Framework for Water Supply and Sanitation Services || 8&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.3 || Coverage and Access to Water Supply Services || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.4|| Policy Environment for Water and Sanitation Services in Tanzania || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.5 || Major Stakeholders in  Water Supply and Sanitation Projects || 10&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.6 || Water Supply and Sanitation Public Private Partnership in Tanzania || 11&lt;br /&gt;
|-&lt;br /&gt;
| 1.3 || Rationale for Preparation of the Fourth Edition DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.4 || About the Fourth Edition of the DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.5 || Organisation of the 4th edition of the DCOM Manual || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.6 || Purpose of this Volume || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.7 || References	 || 15&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
* CHAPTER TWO	17&lt;br /&gt;
* PROJECT PLANNING	17&lt;br /&gt;
* 2.1	Planning Considerations for Water Supply Projects	17&lt;br /&gt;
* 2.2	Project Planning Steps	18&lt;br /&gt;
* 2.3	Pump Protection	18&lt;br /&gt;
* 2.3.1	Initiation	18&lt;br /&gt;
* 2.3.1.1	Community Assessment Steps	20&lt;br /&gt;
* 2.3.1.2	Methods of conducting community assessment	20&lt;br /&gt;
* 2.3.1.2.1	Comprehensive community assessment	20&lt;br /&gt;
* 2.3.1.2.2	Strategic community assessment	20&lt;br /&gt;
* 2.3.2	Pre-feasibility Study	21&lt;br /&gt;
* 2.3.3	Feasibility Study	21&lt;br /&gt;
* 2.3.3.1	Water Supply Projects Ranking and Technology Selection Criteria	22&lt;br /&gt;
* 2.3.3.1.1	Ranking of Projects	22&lt;br /&gt;
* 2.3.3.1.2	Choice of Technology	23&lt;br /&gt;
* 2.3.4	Preliminary and Detailed Design	23&lt;br /&gt;
* 2.3.4.1	Detailed Engineering Drawings	24&lt;br /&gt;
* 2.3.4.2	Detailed estimates of capital costs	24&lt;br /&gt;
* 2.3.4.3	Detailed estimates of recurrent costs	24&lt;br /&gt;
* 2.3.4.4	Anticipated revenue	25&lt;br /&gt;
* 2.3.4.5	Detailed design report	25&lt;br /&gt;
* 2.3.4.6	Project write-up to be submitted to potential financiers	25&lt;br /&gt;
* 2.3.5	Project Phasing	25&lt;br /&gt;
* 2.3.6	Procurement	26&lt;br /&gt;
* 2.3.6.1	2.2.6.1 Preparation of Tender Documents	26&lt;br /&gt;
* 2.3.6.2	Tendering process	27&lt;br /&gt;
* 2.3.7	Implementation/Construction Stage	27&lt;br /&gt;
* 2.3.7.1	Contract Management	27&lt;br /&gt;
* 2.3.7.2	Contract supervision and administration	27&lt;br /&gt;
* 2.3.8	Operation and Maintenance Stage	28&lt;br /&gt;
* 2.3.9	Performance Monitoring	28&lt;br /&gt;
* 2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans	28&lt;br /&gt;
* 2.4.1	Status of Development and Implementation of IWRMD Plans	29&lt;br /&gt;
* 2.4.2	Components of IWRMD Plans	30&lt;br /&gt;
* 2.5	Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change	30&lt;br /&gt;
* 2.6	Environmental and Social Impact Assessment Compliance	30&lt;br /&gt;
* 2.6.1	Procedures for Conducting ESIA in Tanzania	31&lt;br /&gt;
* 2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance	31&lt;br /&gt;
* 2.7	Potential Impacts of Climate Change on Water Supply Projects	32&lt;br /&gt;
* 2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages	32&lt;br /&gt;
* 2.9	References	32&lt;br /&gt;
* CHAPTER THREE	35&lt;br /&gt;
* WATER SOURCES ANALYSIS	35&lt;br /&gt;
* 3.1	Availability of Water Resources in Tanzania Mainland	35&lt;br /&gt;
* 3.2	Water Sources Available in Tanzania Mainland	38&lt;br /&gt;
* 3.2.1	Rainwater and fog harvesting	39&lt;br /&gt;
* 3.2.2	Surface Water	39&lt;br /&gt;
* 3.2.2.1	Rivers or streams	39&lt;br /&gt;
* 3.2.2.2	Impoundments	39&lt;br /&gt;
* 3.2.2.3	Springs	39&lt;br /&gt;
* 3.2.2.4	Lakes	39&lt;br /&gt;
* 3.2.2.5	Dams	40&lt;br /&gt;
* 3.2.3	Groundwater	40&lt;br /&gt;
* 3.2.3.1	Infiltration galleries/wells	40&lt;br /&gt;
* 3.2.3.2	Well	40&lt;br /&gt;
* 3.2.3.3	Classification of wells based on the aquifer tapped	41&lt;br /&gt;
* 3.2.3.3.1	Shallow wells	41&lt;br /&gt;
* 3.2.3.3.2	Deep wells	41&lt;br /&gt;
* 3.2.3.3.3	Artesian wells	41&lt;br /&gt;
* 3.3	Quality Suitability of Water Sources for Water Supply Projects	42&lt;br /&gt;
* 3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment	42&lt;br /&gt;
* 3.5	General Considerations for Selection of Water Sources	42&lt;br /&gt;
* 3.5.1	Adequacy and reliability	42&lt;br /&gt;
* 3.5.2	Quality of water sources	43&lt;br /&gt;
* 3.5.3	Technical Requirements	43&lt;br /&gt;
* 3.5.4	Cost implications to develop a water source	43&lt;br /&gt;
* 3.5.5	Protection of water sources	43&lt;br /&gt;
* 3.5.6	Legal and management requirements	44&lt;br /&gt;
* 3.5.7	Distance of water supply source	44&lt;br /&gt;
* 3.5.8	Topography of the project area and its surroundings	44&lt;br /&gt;
* 3.5.9	Elevation of a source of water supply	44&lt;br /&gt;
* 3.6	Determination of water source yield	44&lt;br /&gt;
* 3.6.1	Rainwater and fog harvesting	45&lt;br /&gt;
* 3.6.1.1	Rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.1	Types of rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.2	Components of rainwater harvesting system	46&lt;br /&gt;
* 3.6.1.1.3	Estimation of the yield	47&lt;br /&gt;
* 3.6.2	Hydrological Analysis of Surface Waters	47&lt;br /&gt;
* 3.7	Other considerations for various water sources	55&lt;br /&gt;
* 3.7.1	Water permits Considerations	55&lt;br /&gt;
* 3.7.2	Conservation of water sources	55&lt;br /&gt;
* 3.8	References	55&lt;br /&gt;
* CHAPTER FOUR	56&lt;br /&gt;
* WATER DEMAND ASSESSMENT	56&lt;br /&gt;
* 4.1	Water Demand Assessment	56&lt;br /&gt;
* 4.2	General Factors Affecting Water Demand Assessment	57&lt;br /&gt;
* 4.3	Determination of Water Demand for Different Uses	58&lt;br /&gt;
* Step 7. Establish Net Water Demand	67&lt;br /&gt;
* Step 9: Establish Operational water consumption	67&lt;br /&gt;
* Step 10: Establish System water losses	68&lt;br /&gt;
* Step 11 Establish Non-Revenue Water	69&lt;br /&gt;
* 4.4	Variations in Water Consumption	70&lt;br /&gt;
* 4.4.1	Definitions	70&lt;br /&gt;
* 4.4.2	Variation in the Rate of Consumption	71&lt;br /&gt;
* 4.4.2.1	Diurnal variation in demand	71&lt;br /&gt;
* 4.4.3	Peak Factors	72&lt;br /&gt;
* 4.4.4	Predicting Demand	74&lt;br /&gt;
* 4.4.5	Design Demand	75&lt;br /&gt;
* 4.5	References	75&lt;br /&gt;
* CHAPTER FIVE	76&lt;br /&gt;
* PIPELINES DESIGN	76&lt;br /&gt;
* 5.1	Design Requirements of pipelines	76&lt;br /&gt;
* 5.2	Types of pipelines	76&lt;br /&gt;
* 5.3	Security considerations for pipelines	76&lt;br /&gt;
* 5.3.1	Methods of water transmission and distribution	76&lt;br /&gt;
* 5.3.2	Gravity flow	77&lt;br /&gt;
* 5.3.3	Pumping with storage	77&lt;br /&gt;
* 5.3.4	Direct pumping to the distribution system	77&lt;br /&gt;
* 5.4	Pipeline Hydraulics Assessment	77&lt;br /&gt;
* 5.4.1	Pressure	77&lt;br /&gt;
* 5.4.2	Determination of Head Losses	77&lt;br /&gt;
* 5.5	Water supply transmission system	79&lt;br /&gt;
* 5.5.1	Determination of Transmission Pipe Size	79&lt;br /&gt;
* 5.5.2	Maximum Pressure	79&lt;br /&gt;
* 5.6	Distribution system	80&lt;br /&gt;
* 5.6.1	Branched System	80&lt;br /&gt;
* 5.6.2	Looped System	81&lt;br /&gt;
* 5.7	Pipe network analysis	82&lt;br /&gt;
* 5.7.1	Network analysis by Conventional method (Hardy Cross)	82&lt;br /&gt;
* 5.7.2	Network Analysis by Computer Software	82&lt;br /&gt;
* 5.7.2.1	EPANET Software	82&lt;br /&gt;
* 5.7.3	Pipeline design criteria	85&lt;br /&gt;
* 5.8	Pipeline materials selection	86&lt;br /&gt;
* 5.8.1	Considerations in Selecting Pipeline Materials	86&lt;br /&gt;
* 5.8.1.1	Flow Characteristics	86&lt;br /&gt;
* 5.8.1.2	Pipe Strength	86&lt;br /&gt;
* 5.8.1.3	Durability	87&lt;br /&gt;
* 5.8.1.4	Type of Soil	87&lt;br /&gt;
* 5.8.1.5	Availability	87&lt;br /&gt;
* 5.8.1.6	Cost of Pipes	87&lt;br /&gt;
* 5.8.2	Types of Pipe Materials Available	87&lt;br /&gt;
* 5.8.2.1	Galvanized Iron (GI) Pipes	87&lt;br /&gt;
* 5.8.2.2	Plastic Pipes	87&lt;br /&gt;
* 5.9	Appurtenances for transmission and distribution mains	88&lt;br /&gt;
* 5.9.1	Valves	89&lt;br /&gt;
* 5.9.1.1	Isolation Valves	89&lt;br /&gt;
* 5.9.1.2	Check Valves	89&lt;br /&gt;
* 5.9.1.3	Float Valves	89&lt;br /&gt;
* 5.9.1.4	Air Release Valves	89&lt;br /&gt;
* 5.9.1.5	Pressure Reducing Valves	89&lt;br /&gt;
* 5.9.1.6	Washout valves	89&lt;br /&gt;
* 5.9.2	Fittings	89&lt;br /&gt;
* 5.10	References	90&lt;br /&gt;
* CHAPTER SIX	91&lt;br /&gt;
* PUMPING SYSTEMS	91&lt;br /&gt;
* 6.1	Introduction	91&lt;br /&gt;
* 6.2	Rationale	91&lt;br /&gt;
* 6.3	Common Types of Pumps used in water supply	91&lt;br /&gt;
* 6.4	Pumping System Setup	91&lt;br /&gt;
* 6.5	Source of Pumping Power	92&lt;br /&gt;
* 6.6	Pumping system design pump selection	92&lt;br /&gt;
* 6.7	Pump Protection	95&lt;br /&gt;
* 6.8	References	95&lt;br /&gt;
* CHAPTER SEVEN	96&lt;br /&gt;
* WATER TREATMENT	96&lt;br /&gt;
* 7.1	Introduction	96&lt;br /&gt;
* 7.1.1	Classification of the qualities of water sources found in Tanzania according to the complexity of its treatment	96&lt;br /&gt;
* 7.1.2	Classification of Unit Operations to achieve water treatment levels	99&lt;br /&gt;
* 7.2	Recommended overall design approach for treatment plant components	99&lt;br /&gt;
* 7.3	Documents and websites consulted and those which are hyper-linked to the DCOM Manual	100&lt;br /&gt;
* 7.4	Water treatment design considerations	100&lt;br /&gt;
* 7.5	Water treatment levels and units	101&lt;br /&gt;
* 7.5.1	Pre-treatment	101&lt;br /&gt;
* 7.5.1.1	Scum and Floating Materials Skimmer	101&lt;br /&gt;
* 7.5.1.2	Screening or straining	101&lt;br /&gt;
* 7.5.1.3	Grit Removal	103&lt;br /&gt;
* 7.5.1.3.1	Design criteria	103&lt;br /&gt;
* 7.5.1.4	Sand Traps	105&lt;br /&gt;
* 7.5.1.5	Pre-chlorination	107&lt;br /&gt;
* 7.5.1.6	Water pre-conditioning (pH adjustment)	108&lt;br /&gt;
* 7.5.2	Primary Treatment	108&lt;br /&gt;
* 7.5.2.1	Sedimentation	108&lt;br /&gt;
* 7.5.2.2	Primary Filtration	114&lt;br /&gt;
* 7.5.2.2.1	Slow Sand Filtration	114&lt;br /&gt;
* 7.5.2.2.2	Rapid Gravity Sand Filtration	117&lt;br /&gt;
* 7.5.2.2.3	Comparison between Slow Sand Filters and Rapid Sand Filters	118&lt;br /&gt;
* 7.5.2.2.4	Other Types of Filters	119&lt;br /&gt;
* 7.5.2.3	Floatation	124&lt;br /&gt;
* 7.5.2.3.1	Dissolved-Air Floatation	124&lt;br /&gt;
* 7.5.2.3.2	Electrolytic Floatation	125&lt;br /&gt;
* 7.5.2.3.3	Dispersed-Air Floatation	125&lt;br /&gt;
* 7.5.2.4	Aeration	125&lt;br /&gt;
* 7.5.2.4.1	Falling Water Aerators	126&lt;br /&gt;
* 7.5.2.4.2	Spray Aerators	127&lt;br /&gt;
* 7.5.3	Secondary Treatment	130&lt;br /&gt;
* 7.5.3.1	Clarification	130&lt;br /&gt;
* 7.5.3.2	Coagulation	130&lt;br /&gt;
* 7.5.3.3	Flocculation	131&lt;br /&gt;
* 7.5.3.4	Filtration	131&lt;br /&gt;
* 7.5.4	Tertiary Treatment	132&lt;br /&gt;
* 7.5.4.1	Disinfection	132&lt;br /&gt;
* 7.5.4.1.1	Disinfection Methods	132&lt;br /&gt;
* 7.5.4.1.2	Chlorinators	132&lt;br /&gt;
* 7.5.4.1.3	Design considerations for chlorinators	133&lt;br /&gt;
* 7.5.4.2	Ozonation	133&lt;br /&gt;
* 7.5.4.3	Water softening	134&lt;br /&gt;
* 7.5.4.3.1	Methods of Softening	135&lt;br /&gt;
* 7.5.4.4	Defluoridation of Water	139&lt;br /&gt;
* 7.5.4.4.1	Fluorides	139&lt;br /&gt;
* 7.5.4.4.2	Defluoridation	139&lt;br /&gt;
* 7.5.4.5	Water Conditioning	141&lt;br /&gt;
* 7.5.5	Managemen&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=490</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=490"/>
		<updated>2020-03-30T18:52:31Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! # !! Title !! Page&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[CHAPTER ONE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[CHAPTER TWO: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[CHAPTER THREE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[CHAPTER FOUR: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[CHAPTER FIVE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[CHAPTER SIX: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[CHAPTER SEVEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[CHAPTER EIGHT: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[CHAPTER NINE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[CHAPTER TEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[CHAPTER ELEVEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[CHAPTER TWELVE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[CHAPTER THIRTEEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[APENDICES: APPENDICES]] || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Chapter #!! Chapter Title!! Page&lt;br /&gt;
|-&lt;br /&gt;
| i || LIST OF SPECIAL COMMITTEE MEMBERS || V&lt;br /&gt;
|-&lt;br /&gt;
| 1|| CHAPTER ONE: INTRODUCTION		 || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1|| Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.1 || Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.2 || Climate Change and Resilience to Climate Change || 2&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.3 || Public-Private Partnership in Water Supply and Sanitation Projects in Developing Countries || 3&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.4 || International Water Law || 4&lt;br /&gt;
|-&lt;br /&gt;
| 1.2 || Development Agenda and Water and Sanitation Sector in Tanzania || 5&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.1 || National Water Policy || 7&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.2|| Legal and Institutional Framework for Water Supply and Sanitation Services || 8&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.3 || Coverage and Access to Water Supply Services || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.4|| Policy Environment for Water and Sanitation Services in Tanzania || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.5 || Major Stakeholders in  Water Supply and Sanitation Projects || 10&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.6 || Water Supply and Sanitation Public Private Partnership in Tanzania || 11&lt;br /&gt;
|-&lt;br /&gt;
| 1.3 || Rationale for Preparation of the Fourth Edition DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.4 || About the Fourth Edition of the DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.5 || Organisation of the 4th edition of the DCOM Manual || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.6 || Purpose of this Volume || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.7 || References	 || 15&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
* CHAPTER TWO	17&lt;br /&gt;
* PROJECT PLANNING	17&lt;br /&gt;
* 2.1	Planning Considerations for Water Supply Projects	17&lt;br /&gt;
* 2.2	Project Planning Steps	18&lt;br /&gt;
* 2.3	Pump Protection	18&lt;br /&gt;
* 2.3.1	Initiation	18&lt;br /&gt;
* 2.3.1.1	Community Assessment Steps	20&lt;br /&gt;
* 2.3.1.2	Methods of conducting community assessment	20&lt;br /&gt;
* 2.3.1.2.1	Comprehensive community assessment	20&lt;br /&gt;
* 2.3.1.2.2	Strategic community assessment	20&lt;br /&gt;
* 2.3.2	Pre-feasibility Study	21&lt;br /&gt;
* 2.3.3	Feasibility Study	21&lt;br /&gt;
* 2.3.3.1	Water Supply Projects Ranking and Technology Selection Criteria	22&lt;br /&gt;
* 2.3.3.1.1	Ranking of Projects	22&lt;br /&gt;
* 2.3.3.1.2	Choice of Technology	23&lt;br /&gt;
* 2.3.4	Preliminary and Detailed Design	23&lt;br /&gt;
* 2.3.4.1	Detailed Engineering Drawings	24&lt;br /&gt;
* 2.3.4.2	Detailed estimates of capital costs	24&lt;br /&gt;
* 2.3.4.3	Detailed estimates of recurrent costs	24&lt;br /&gt;
* 2.3.4.4	Anticipated revenue	25&lt;br /&gt;
* 2.3.4.5	Detailed design report	25&lt;br /&gt;
* 2.3.4.6	Project write-up to be submitted to potential financiers	25&lt;br /&gt;
* 2.3.5	Project Phasing	25&lt;br /&gt;
* 2.3.6	Procurement	26&lt;br /&gt;
* 2.3.6.1	2.2.6.1 Preparation of Tender Documents	26&lt;br /&gt;
* 2.3.6.2	Tendering process	27&lt;br /&gt;
* 2.3.7	Implementation/Construction Stage	27&lt;br /&gt;
* 2.3.7.1	Contract Management	27&lt;br /&gt;
* 2.3.7.2	Contract supervision and administration	27&lt;br /&gt;
* 2.3.8	Operation and Maintenance Stage	28&lt;br /&gt;
* 2.3.9	Performance Monitoring	28&lt;br /&gt;
* 2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans	28&lt;br /&gt;
* 2.4.1	Status of Development and Implementation of IWRMD Plans	29&lt;br /&gt;
* 2.4.2	Components of IWRMD Plans	30&lt;br /&gt;
* 2.5	Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change	30&lt;br /&gt;
* 2.6	Environmental and Social Impact Assessment Compliance	30&lt;br /&gt;
* 2.6.1	Procedures for Conducting ESIA in Tanzania	31&lt;br /&gt;
* 2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance	31&lt;br /&gt;
* 2.7	Potential Impacts of Climate Change on Water Supply Projects	32&lt;br /&gt;
* 2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages	32&lt;br /&gt;
* 2.9	References	32&lt;br /&gt;
* CHAPTER THREE	35&lt;br /&gt;
* WATER SOURCES ANALYSIS	35&lt;br /&gt;
* 3.1	Availability of Water Resources in Tanzania Mainland	35&lt;br /&gt;
* 3.2	Water Sources Available in Tanzania Mainland	38&lt;br /&gt;
* 3.2.1	Rainwater and fog harvesting	39&lt;br /&gt;
* 3.2.2	Surface Water	39&lt;br /&gt;
* 3.2.2.1	Rivers or streams	39&lt;br /&gt;
* 3.2.2.2	Impoundments	39&lt;br /&gt;
* 3.2.2.3	Springs	39&lt;br /&gt;
* 3.2.2.4	Lakes	39&lt;br /&gt;
* 3.2.2.5	Dams	40&lt;br /&gt;
* 3.2.3	Groundwater	40&lt;br /&gt;
* 3.2.3.1	Infiltration galleries/wells	40&lt;br /&gt;
* 3.2.3.2	Well	40&lt;br /&gt;
* 3.2.3.3	Classification of wells based on the aquifer tapped	41&lt;br /&gt;
* 3.2.3.3.1	Shallow wells	41&lt;br /&gt;
* 3.2.3.3.2	Deep wells	41&lt;br /&gt;
* 3.2.3.3.3	Artesian wells	41&lt;br /&gt;
* 3.3	Quality Suitability of Water Sources for Water Supply Projects	42&lt;br /&gt;
* 3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment	42&lt;br /&gt;
* 3.5	General Considerations for Selection of Water Sources	42&lt;br /&gt;
* 3.5.1	Adequacy and reliability	42&lt;br /&gt;
* 3.5.2	Quality of water sources	43&lt;br /&gt;
* 3.5.3	Technical Requirements	43&lt;br /&gt;
* 3.5.4	Cost implications to develop a water source	43&lt;br /&gt;
* 3.5.5	Protection of water sources	43&lt;br /&gt;
* 3.5.6	Legal and management requirements	44&lt;br /&gt;
* 3.5.7	Distance of water supply source	44&lt;br /&gt;
* 3.5.8	Topography of the project area and its surroundings	44&lt;br /&gt;
* 3.5.9	Elevation of a source of water supply	44&lt;br /&gt;
* 3.6	Determination of water source yield	44&lt;br /&gt;
* 3.6.1	Rainwater and fog harvesting	45&lt;br /&gt;
* 3.6.1.1	Rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.1	Types of rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.2	Components of rainwater harvesting system	46&lt;br /&gt;
* 3.6.1.1.3	Estimation of the yield	47&lt;br /&gt;
* 3.6.2	Hydrological Analysis of Surface Waters	47&lt;br /&gt;
* 3.7	Other considerations for various water sources	55&lt;br /&gt;
* 3.7.1	Water permits Considerations	55&lt;br /&gt;
* 3.7.2	Conservation of water sources	55&lt;br /&gt;
* 3.8	References	55&lt;br /&gt;
* CHAPTER FOUR	56&lt;br /&gt;
* WATER DEMAND ASSESSMENT	56&lt;br /&gt;
* 4.1	Water Demand Assessment	56&lt;br /&gt;
* 4.2	General Factors Affecting Water Demand Assessment	57&lt;br /&gt;
* 4.3	Determination of Water Demand for Different Uses	58&lt;br /&gt;
* Step 7. Establish Net Water Demand	67&lt;br /&gt;
* Step 9: Establish Operational water consumption	67&lt;br /&gt;
* Step 10: Establish System water losses	68&lt;br /&gt;
* Step 11 Establish Non-Revenue Water	69&lt;br /&gt;
* 4.4	Variations in Water Consumption	70&lt;br /&gt;
* 4.4.1	Definitions	70&lt;br /&gt;
* 4.4.2	Variation in the Rate of Consumption	71&lt;br /&gt;
* 4.4.2.1	Diurnal variation in demand	71&lt;br /&gt;
* 4.4.3	Peak Factors	72&lt;br /&gt;
* 4.4.4	Predicting Demand	74&lt;br /&gt;
* 4.4.5	Design Demand	75&lt;br /&gt;
* 4.5	References	75&lt;br /&gt;
* CHAPTER FIVE	76&lt;br /&gt;
* PIPELINES DESIGN	76&lt;br /&gt;
* 5.1	Design Requirements of pipelines	76&lt;br /&gt;
* 5.2	Types of pipelines	76&lt;br /&gt;
* 5.3	Security considerations for pipelines	76&lt;br /&gt;
* 5.3.1	Methods of water transmission and distribution	76&lt;br /&gt;
* 5.3.2	Gravity flow	77&lt;br /&gt;
* 5.3.3	Pumping with storage	77&lt;br /&gt;
* 5.3.4	Direct pumping to the distribution system	77&lt;br /&gt;
* 5.4	Pipeline Hydraulics Assessment	77&lt;br /&gt;
* 5.4.1	Pressure	77&lt;br /&gt;
* 5.4.2	Determination of Head Losses	77&lt;br /&gt;
* 5.5	Water supply transmission system	79&lt;br /&gt;
* 5.5.1	Determination of Transmission Pipe Size	79&lt;br /&gt;
* 5.5.2	Maximum Pressure	79&lt;br /&gt;
* 5.6	Distribution system	80&lt;br /&gt;
* 5.6.1	Branched System	80&lt;br /&gt;
* 5.6.2	Looped System	81&lt;br /&gt;
* 5.7	Pipe network analysis	82&lt;br /&gt;
* 5.7.1	Network analysis by Conventional method (Hardy Cross)	82&lt;br /&gt;
* 5.7.2	Network Analysis by Computer Software	82&lt;br /&gt;
* 5.7.2.1	EPANET Software	82&lt;br /&gt;
* 5.7.3	Pipeline design criteria	85&lt;br /&gt;
* 5.8	Pipeline materials selection	86&lt;br /&gt;
* 5.8.1	Considerations in Selecting Pipeline Materials	86&lt;br /&gt;
* 5.8.1.1	Flow Characteristics	86&lt;br /&gt;
* 5.8.1.2	Pipe Strength	86&lt;br /&gt;
* 5.8.1.3	Durability	87&lt;br /&gt;
* 5.8.1.4	Type of Soil	87&lt;br /&gt;
* 5.8.1.5	Availability	87&lt;br /&gt;
* 5.8.1.6	Cost of Pipes	87&lt;br /&gt;
* 5.8.2	Types of Pipe Materials Available	87&lt;br /&gt;
* 5.8.2.1	Galvanized Iron (GI) Pipes	87&lt;br /&gt;
* 5.8.2.2	Plastic Pipes	87&lt;br /&gt;
* 5.9	Appurtenances for transmission and distribution mains	88&lt;br /&gt;
* 5.9.1	Valves	89&lt;br /&gt;
* 5.9.1.1	Isolation Valves	89&lt;br /&gt;
* 5.9.1.2	Check Valves	89&lt;br /&gt;
* 5.9.1.3	Float Valves	89&lt;br /&gt;
* 5.9.1.4	Air Release Valves	89&lt;br /&gt;
* 5.9.1.5	Pressure Reducing Valves	89&lt;br /&gt;
* 5.9.1.6	Washout valves	89&lt;br /&gt;
* 5.9.2	Fittings	89&lt;br /&gt;
* 5.10	References	90&lt;br /&gt;
* CHAPTER SIX	91&lt;br /&gt;
* PUMPING SYSTEMS	91&lt;br /&gt;
* 6.1	Introduction	91&lt;br /&gt;
* 6.2	Rationale	91&lt;br /&gt;
* 6.3	Common Types of Pumps used in water supply	91&lt;br /&gt;
* 6.4	Pumping System Setup	91&lt;br /&gt;
* 6.5	Source of Pumping Power	92&lt;br /&gt;
* 6.6	Pumping system design pump selection	92&lt;br /&gt;
* 6.7	Pump Protection	95&lt;br /&gt;
* 6.8	References	95&lt;br /&gt;
* CHAPTER SEVEN	96&lt;br /&gt;
* WATER TREATMENT	96&lt;br /&gt;
* 7.1	Introduction	96&lt;br /&gt;
* 7.1.1	Classification of the qualities of water sources found in Tanzania according to the complexity of its treatment	96&lt;br /&gt;
* 7.1.2	Classification of Unit Operations to achieve water treatment levels	99&lt;br /&gt;
* 7.2	Recommended overall design approach for treatment plant components	99&lt;br /&gt;
* 7.3	Documents and websites consulted and those which are hyper-linked to the DCOM Manual	100&lt;br /&gt;
* 7.4	Water treatment design considerations	100&lt;br /&gt;
* 7.5	Water treatment levels and units	101&lt;br /&gt;
* 7.5.1	Pre-treatment	101&lt;br /&gt;
* 7.5.1.1	Scum and Floating Materials Skimmer	101&lt;br /&gt;
* 7.5.1.2	Screening or straining	101&lt;br /&gt;
* 7.5.1.3	Grit Removal	103&lt;br /&gt;
* 7.5.1.3.1	Design criteria	103&lt;br /&gt;
* 7.5.1.4	Sand Traps	105&lt;br /&gt;
* 7.5.1.5	Pre-chlorination	107&lt;br /&gt;
* 7.5.1.6	Water pre-conditioning (pH adjustment)	108&lt;br /&gt;
* 7.5.2	Primary Treatment	108&lt;br /&gt;
* 7.5.2.1	Sedimentation	108&lt;br /&gt;
* 7.5.2.2	Primary Filtration	114&lt;br /&gt;
* 7.5.2.2.1	Slow Sand Filtration	114&lt;br /&gt;
* 7.5.2.2.2	Rapid Gravity Sand Filtration	117&lt;br /&gt;
* 7.5.2.2.3	Comparison between Slow Sand Filters and Rapid Sand Filters	118&lt;br /&gt;
* 7.5.2.2.4	Other Types of Filters	119&lt;br /&gt;
* 7.5.2.3	Floatation	124&lt;br /&gt;
* 7.5.2.3.1	Dissolved-Air Floatation	124&lt;br /&gt;
* 7.5.2.3.2	Electrolytic Floatation	125&lt;br /&gt;
* 7.5.2.3.3	Dispersed-Air Floatation	125&lt;br /&gt;
* 7.5.2.4	Aeration	125&lt;br /&gt;
* 7.5.2.4.1	Falling Water Aerators	126&lt;br /&gt;
* 7.5.2.4.2	Spray Aerators	127&lt;br /&gt;
* 7.5.3	Secondary Treatment	130&lt;br /&gt;
* 7.5.3.1	Clarification	130&lt;br /&gt;
* 7.5.3.2	Coagulation	130&lt;br /&gt;
* 7.5.3.3	Flocculation	131&lt;br /&gt;
* 7.5.3.4	Filtration	131&lt;br /&gt;
* 7.5.4	Tertiary Treatment	132&lt;br /&gt;
* 7.5.4.1	Disinfection	132&lt;br /&gt;
* 7.5.4.1.1	Disinfection Methods	132&lt;br /&gt;
* 7.5.4.1.2	Chlorinators	132&lt;br /&gt;
* 7.5.4.1.3	Design considerations for chlorinators	133&lt;br /&gt;
* 7.5.4.2	Ozonation	133&lt;br /&gt;
* 7.5.4.3	Water softening	134&lt;br /&gt;
* 7.5.4.3.1	Methods of Softening	135&lt;br /&gt;
* 7.5.4.4	Defluoridation of Water	139&lt;br /&gt;
* 7.5.4.4.1	Fluorides	139&lt;br /&gt;
* 7.5.4.4.2	Defluoridation	139&lt;br /&gt;
* 7.5.4.5	Water Conditioning	141&lt;br /&gt;
* 7.5.5	Managemen&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=489</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=489"/>
		<updated>2020-03-30T18:51:33Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Header text !! Header text !! Header text&lt;br /&gt;
|-&lt;br /&gt;
| 1 || [[CHAPTER ONE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || 1&lt;br /&gt;
|-&lt;br /&gt;
| 2 || [[CHAPTER TWO: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 3 || [[CHAPTER THREE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 4 || [[CHAPTER FOUR: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 5 || [[CHAPTER FIVE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 6 || [[CHAPTER SIX: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 7 || [[CHAPTER SEVEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 8 || [[CHAPTER EIGHT: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 9 || [[CHAPTER NINE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 10 || [[CHAPTER TEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 11 || [[CHAPTER ELEVEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 12 || [[CHAPTER TWELVE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 13 || [[CHAPTER THIRTEEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| 14 || [[APENDICES: APPENDICES]] || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Chapter #!! Chapter Title!! Page&lt;br /&gt;
|-&lt;br /&gt;
| i || LIST OF SPECIAL COMMITTEE MEMBERS || V&lt;br /&gt;
|-&lt;br /&gt;
| 1|| CHAPTER ONE: INTRODUCTION		 || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1|| Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.1 || Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.2 || Climate Change and Resilience to Climate Change || 2&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.3 || Public-Private Partnership in Water Supply and Sanitation Projects in Developing Countries || 3&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.4 || International Water Law || 4&lt;br /&gt;
|-&lt;br /&gt;
| 1.2 || Development Agenda and Water and Sanitation Sector in Tanzania || 5&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.1 || National Water Policy || 7&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.2|| Legal and Institutional Framework for Water Supply and Sanitation Services || 8&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.3 || Coverage and Access to Water Supply Services || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.4|| Policy Environment for Water and Sanitation Services in Tanzania || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.5 || Major Stakeholders in  Water Supply and Sanitation Projects || 10&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.6 || Water Supply and Sanitation Public Private Partnership in Tanzania || 11&lt;br /&gt;
|-&lt;br /&gt;
| 1.3 || Rationale for Preparation of the Fourth Edition DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.4 || About the Fourth Edition of the DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.5 || Organisation of the 4th edition of the DCOM Manual || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.6 || Purpose of this Volume || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.7 || References	 || 15&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
* CHAPTER TWO	17&lt;br /&gt;
* PROJECT PLANNING	17&lt;br /&gt;
* 2.1	Planning Considerations for Water Supply Projects	17&lt;br /&gt;
* 2.2	Project Planning Steps	18&lt;br /&gt;
* 2.3	Pump Protection	18&lt;br /&gt;
* 2.3.1	Initiation	18&lt;br /&gt;
* 2.3.1.1	Community Assessment Steps	20&lt;br /&gt;
* 2.3.1.2	Methods of conducting community assessment	20&lt;br /&gt;
* 2.3.1.2.1	Comprehensive community assessment	20&lt;br /&gt;
* 2.3.1.2.2	Strategic community assessment	20&lt;br /&gt;
* 2.3.2	Pre-feasibility Study	21&lt;br /&gt;
* 2.3.3	Feasibility Study	21&lt;br /&gt;
* 2.3.3.1	Water Supply Projects Ranking and Technology Selection Criteria	22&lt;br /&gt;
* 2.3.3.1.1	Ranking of Projects	22&lt;br /&gt;
* 2.3.3.1.2	Choice of Technology	23&lt;br /&gt;
* 2.3.4	Preliminary and Detailed Design	23&lt;br /&gt;
* 2.3.4.1	Detailed Engineering Drawings	24&lt;br /&gt;
* 2.3.4.2	Detailed estimates of capital costs	24&lt;br /&gt;
* 2.3.4.3	Detailed estimates of recurrent costs	24&lt;br /&gt;
* 2.3.4.4	Anticipated revenue	25&lt;br /&gt;
* 2.3.4.5	Detailed design report	25&lt;br /&gt;
* 2.3.4.6	Project write-up to be submitted to potential financiers	25&lt;br /&gt;
* 2.3.5	Project Phasing	25&lt;br /&gt;
* 2.3.6	Procurement	26&lt;br /&gt;
* 2.3.6.1	2.2.6.1 Preparation of Tender Documents	26&lt;br /&gt;
* 2.3.6.2	Tendering process	27&lt;br /&gt;
* 2.3.7	Implementation/Construction Stage	27&lt;br /&gt;
* 2.3.7.1	Contract Management	27&lt;br /&gt;
* 2.3.7.2	Contract supervision and administration	27&lt;br /&gt;
* 2.3.8	Operation and Maintenance Stage	28&lt;br /&gt;
* 2.3.9	Performance Monitoring	28&lt;br /&gt;
* 2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans	28&lt;br /&gt;
* 2.4.1	Status of Development and Implementation of IWRMD Plans	29&lt;br /&gt;
* 2.4.2	Components of IWRMD Plans	30&lt;br /&gt;
* 2.5	Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change	30&lt;br /&gt;
* 2.6	Environmental and Social Impact Assessment Compliance	30&lt;br /&gt;
* 2.6.1	Procedures for Conducting ESIA in Tanzania	31&lt;br /&gt;
* 2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance	31&lt;br /&gt;
* 2.7	Potential Impacts of Climate Change on Water Supply Projects	32&lt;br /&gt;
* 2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages	32&lt;br /&gt;
* 2.9	References	32&lt;br /&gt;
* CHAPTER THREE	35&lt;br /&gt;
* WATER SOURCES ANALYSIS	35&lt;br /&gt;
* 3.1	Availability of Water Resources in Tanzania Mainland	35&lt;br /&gt;
* 3.2	Water Sources Available in Tanzania Mainland	38&lt;br /&gt;
* 3.2.1	Rainwater and fog harvesting	39&lt;br /&gt;
* 3.2.2	Surface Water	39&lt;br /&gt;
* 3.2.2.1	Rivers or streams	39&lt;br /&gt;
* 3.2.2.2	Impoundments	39&lt;br /&gt;
* 3.2.2.3	Springs	39&lt;br /&gt;
* 3.2.2.4	Lakes	39&lt;br /&gt;
* 3.2.2.5	Dams	40&lt;br /&gt;
* 3.2.3	Groundwater	40&lt;br /&gt;
* 3.2.3.1	Infiltration galleries/wells	40&lt;br /&gt;
* 3.2.3.2	Well	40&lt;br /&gt;
* 3.2.3.3	Classification of wells based on the aquifer tapped	41&lt;br /&gt;
* 3.2.3.3.1	Shallow wells	41&lt;br /&gt;
* 3.2.3.3.2	Deep wells	41&lt;br /&gt;
* 3.2.3.3.3	Artesian wells	41&lt;br /&gt;
* 3.3	Quality Suitability of Water Sources for Water Supply Projects	42&lt;br /&gt;
* 3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment	42&lt;br /&gt;
* 3.5	General Considerations for Selection of Water Sources	42&lt;br /&gt;
* 3.5.1	Adequacy and reliability	42&lt;br /&gt;
* 3.5.2	Quality of water sources	43&lt;br /&gt;
* 3.5.3	Technical Requirements	43&lt;br /&gt;
* 3.5.4	Cost implications to develop a water source	43&lt;br /&gt;
* 3.5.5	Protection of water sources	43&lt;br /&gt;
* 3.5.6	Legal and management requirements	44&lt;br /&gt;
* 3.5.7	Distance of water supply source	44&lt;br /&gt;
* 3.5.8	Topography of the project area and its surroundings	44&lt;br /&gt;
* 3.5.9	Elevation of a source of water supply	44&lt;br /&gt;
* 3.6	Determination of water source yield	44&lt;br /&gt;
* 3.6.1	Rainwater and fog harvesting	45&lt;br /&gt;
* 3.6.1.1	Rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.1	Types of rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.2	Components of rainwater harvesting system	46&lt;br /&gt;
* 3.6.1.1.3	Estimation of the yield	47&lt;br /&gt;
* 3.6.2	Hydrological Analysis of Surface Waters	47&lt;br /&gt;
* 3.7	Other considerations for various water sources	55&lt;br /&gt;
* 3.7.1	Water permits Considerations	55&lt;br /&gt;
* 3.7.2	Conservation of water sources	55&lt;br /&gt;
* 3.8	References	55&lt;br /&gt;
* CHAPTER FOUR	56&lt;br /&gt;
* WATER DEMAND ASSESSMENT	56&lt;br /&gt;
* 4.1	Water Demand Assessment	56&lt;br /&gt;
* 4.2	General Factors Affecting Water Demand Assessment	57&lt;br /&gt;
* 4.3	Determination of Water Demand for Different Uses	58&lt;br /&gt;
* Step 7. Establish Net Water Demand	67&lt;br /&gt;
* Step 9: Establish Operational water consumption	67&lt;br /&gt;
* Step 10: Establish System water losses	68&lt;br /&gt;
* Step 11 Establish Non-Revenue Water	69&lt;br /&gt;
* 4.4	Variations in Water Consumption	70&lt;br /&gt;
* 4.4.1	Definitions	70&lt;br /&gt;
* 4.4.2	Variation in the Rate of Consumption	71&lt;br /&gt;
* 4.4.2.1	Diurnal variation in demand	71&lt;br /&gt;
* 4.4.3	Peak Factors	72&lt;br /&gt;
* 4.4.4	Predicting Demand	74&lt;br /&gt;
* 4.4.5	Design Demand	75&lt;br /&gt;
* 4.5	References	75&lt;br /&gt;
* CHAPTER FIVE	76&lt;br /&gt;
* PIPELINES DESIGN	76&lt;br /&gt;
* 5.1	Design Requirements of pipelines	76&lt;br /&gt;
* 5.2	Types of pipelines	76&lt;br /&gt;
* 5.3	Security considerations for pipelines	76&lt;br /&gt;
* 5.3.1	Methods of water transmission and distribution	76&lt;br /&gt;
* 5.3.2	Gravity flow	77&lt;br /&gt;
* 5.3.3	Pumping with storage	77&lt;br /&gt;
* 5.3.4	Direct pumping to the distribution system	77&lt;br /&gt;
* 5.4	Pipeline Hydraulics Assessment	77&lt;br /&gt;
* 5.4.1	Pressure	77&lt;br /&gt;
* 5.4.2	Determination of Head Losses	77&lt;br /&gt;
* 5.5	Water supply transmission system	79&lt;br /&gt;
* 5.5.1	Determination of Transmission Pipe Size	79&lt;br /&gt;
* 5.5.2	Maximum Pressure	79&lt;br /&gt;
* 5.6	Distribution system	80&lt;br /&gt;
* 5.6.1	Branched System	80&lt;br /&gt;
* 5.6.2	Looped System	81&lt;br /&gt;
* 5.7	Pipe network analysis	82&lt;br /&gt;
* 5.7.1	Network analysis by Conventional method (Hardy Cross)	82&lt;br /&gt;
* 5.7.2	Network Analysis by Computer Software	82&lt;br /&gt;
* 5.7.2.1	EPANET Software	82&lt;br /&gt;
* 5.7.3	Pipeline design criteria	85&lt;br /&gt;
* 5.8	Pipeline materials selection	86&lt;br /&gt;
* 5.8.1	Considerations in Selecting Pipeline Materials	86&lt;br /&gt;
* 5.8.1.1	Flow Characteristics	86&lt;br /&gt;
* 5.8.1.2	Pipe Strength	86&lt;br /&gt;
* 5.8.1.3	Durability	87&lt;br /&gt;
* 5.8.1.4	Type of Soil	87&lt;br /&gt;
* 5.8.1.5	Availability	87&lt;br /&gt;
* 5.8.1.6	Cost of Pipes	87&lt;br /&gt;
* 5.8.2	Types of Pipe Materials Available	87&lt;br /&gt;
* 5.8.2.1	Galvanized Iron (GI) Pipes	87&lt;br /&gt;
* 5.8.2.2	Plastic Pipes	87&lt;br /&gt;
* 5.9	Appurtenances for transmission and distribution mains	88&lt;br /&gt;
* 5.9.1	Valves	89&lt;br /&gt;
* 5.9.1.1	Isolation Valves	89&lt;br /&gt;
* 5.9.1.2	Check Valves	89&lt;br /&gt;
* 5.9.1.3	Float Valves	89&lt;br /&gt;
* 5.9.1.4	Air Release Valves	89&lt;br /&gt;
* 5.9.1.5	Pressure Reducing Valves	89&lt;br /&gt;
* 5.9.1.6	Washout valves	89&lt;br /&gt;
* 5.9.2	Fittings	89&lt;br /&gt;
* 5.10	References	90&lt;br /&gt;
* CHAPTER SIX	91&lt;br /&gt;
* PUMPING SYSTEMS	91&lt;br /&gt;
* 6.1	Introduction	91&lt;br /&gt;
* 6.2	Rationale	91&lt;br /&gt;
* 6.3	Common Types of Pumps used in water supply	91&lt;br /&gt;
* 6.4	Pumping System Setup	91&lt;br /&gt;
* 6.5	Source of Pumping Power	92&lt;br /&gt;
* 6.6	Pumping system design pump selection	92&lt;br /&gt;
* 6.7	Pump Protection	95&lt;br /&gt;
* 6.8	References	95&lt;br /&gt;
* CHAPTER SEVEN	96&lt;br /&gt;
* WATER TREATMENT	96&lt;br /&gt;
* 7.1	Introduction	96&lt;br /&gt;
* 7.1.1	Classification of the qualities of water sources found in Tanzania according to the complexity of its treatment	96&lt;br /&gt;
* 7.1.2	Classification of Unit Operations to achieve water treatment levels	99&lt;br /&gt;
* 7.2	Recommended overall design approach for treatment plant components	99&lt;br /&gt;
* 7.3	Documents and websites consulted and those which are hyper-linked to the DCOM Manual	100&lt;br /&gt;
* 7.4	Water treatment design considerations	100&lt;br /&gt;
* 7.5	Water treatment levels and units	101&lt;br /&gt;
* 7.5.1	Pre-treatment	101&lt;br /&gt;
* 7.5.1.1	Scum and Floating Materials Skimmer	101&lt;br /&gt;
* 7.5.1.2	Screening or straining	101&lt;br /&gt;
* 7.5.1.3	Grit Removal	103&lt;br /&gt;
* 7.5.1.3.1	Design criteria	103&lt;br /&gt;
* 7.5.1.4	Sand Traps	105&lt;br /&gt;
* 7.5.1.5	Pre-chlorination	107&lt;br /&gt;
* 7.5.1.6	Water pre-conditioning (pH adjustment)	108&lt;br /&gt;
* 7.5.2	Primary Treatment	108&lt;br /&gt;
* 7.5.2.1	Sedimentation	108&lt;br /&gt;
* 7.5.2.2	Primary Filtration	114&lt;br /&gt;
* 7.5.2.2.1	Slow Sand Filtration	114&lt;br /&gt;
* 7.5.2.2.2	Rapid Gravity Sand Filtration	117&lt;br /&gt;
* 7.5.2.2.3	Comparison between Slow Sand Filters and Rapid Sand Filters	118&lt;br /&gt;
* 7.5.2.2.4	Other Types of Filters	119&lt;br /&gt;
* 7.5.2.3	Floatation	124&lt;br /&gt;
* 7.5.2.3.1	Dissolved-Air Floatation	124&lt;br /&gt;
* 7.5.2.3.2	Electrolytic Floatation	125&lt;br /&gt;
* 7.5.2.3.3	Dispersed-Air Floatation	125&lt;br /&gt;
* 7.5.2.4	Aeration	125&lt;br /&gt;
* 7.5.2.4.1	Falling Water Aerators	126&lt;br /&gt;
* 7.5.2.4.2	Spray Aerators	127&lt;br /&gt;
* 7.5.3	Secondary Treatment	130&lt;br /&gt;
* 7.5.3.1	Clarification	130&lt;br /&gt;
* 7.5.3.2	Coagulation	130&lt;br /&gt;
* 7.5.3.3	Flocculation	131&lt;br /&gt;
* 7.5.3.4	Filtration	131&lt;br /&gt;
* 7.5.4	Tertiary Treatment	132&lt;br /&gt;
* 7.5.4.1	Disinfection	132&lt;br /&gt;
* 7.5.4.1.1	Disinfection Methods	132&lt;br /&gt;
* 7.5.4.1.2	Chlorinators	132&lt;br /&gt;
* 7.5.4.1.3	Design considerations for chlorinators	133&lt;br /&gt;
* 7.5.4.2	Ozonation	133&lt;br /&gt;
* 7.5.4.3	Water softening	134&lt;br /&gt;
* 7.5.4.3.1	Methods of Softening	135&lt;br /&gt;
* 7.5.4.4	Defluoridation of Water	139&lt;br /&gt;
* 7.5.4.4.1	Fluorides	139&lt;br /&gt;
* 7.5.4.4.2	Defluoridation	139&lt;br /&gt;
* 7.5.4.5	Water Conditioning	141&lt;br /&gt;
* 7.5.5	Managemen&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=488</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=488"/>
		<updated>2020-03-30T18:49:53Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Header text !! Header text !! Header text&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER ONE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
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| Example || [[CHAPTER TWO: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER THREE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER FOUR: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER FIVE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
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| Example || [[CHAPTER SIX: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
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| Example || [[CHAPTER SEVEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER EIGHT: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
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| Example || [[CHAPTER NINE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER TEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER ELEVEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER TWELVE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER THIRTEEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[APENDICES: APPENDICES]] || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Chapter #!! Chapter Title!! Page&lt;br /&gt;
|-&lt;br /&gt;
| i || LIST OF SPECIAL COMMITTEE MEMBERS || V&lt;br /&gt;
|-&lt;br /&gt;
| 1|| CHAPTER ONE: INTRODUCTION		 || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1|| Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.1 || Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.2 || Climate Change and Resilience to Climate Change || 2&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.3 || Public-Private Partnership in Water Supply and Sanitation Projects in Developing Countries || 3&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.4 || International Water Law || 4&lt;br /&gt;
|-&lt;br /&gt;
| 1.2 || Development Agenda and Water and Sanitation Sector in Tanzania || 5&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.1 || National Water Policy || 7&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.2|| Legal and Institutional Framework for Water Supply and Sanitation Services || 8&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.3 || Coverage and Access to Water Supply Services || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.4|| Policy Environment for Water and Sanitation Services in Tanzania || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.5 || Major Stakeholders in  Water Supply and Sanitation Projects || 10&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.6 || Water Supply and Sanitation Public Private Partnership in Tanzania || 11&lt;br /&gt;
|-&lt;br /&gt;
| 1.3 || Rationale for Preparation of the Fourth Edition DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.4 || About the Fourth Edition of the DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.5 || Organisation of the 4th edition of the DCOM Manual || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.6 || Purpose of this Volume || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.7 || References	 || 15&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
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|}&lt;br /&gt;
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&lt;br /&gt;
* CHAPTER TWO	17&lt;br /&gt;
* PROJECT PLANNING	17&lt;br /&gt;
* 2.1	Planning Considerations for Water Supply Projects	17&lt;br /&gt;
* 2.2	Project Planning Steps	18&lt;br /&gt;
* 2.3	Pump Protection	18&lt;br /&gt;
* 2.3.1	Initiation	18&lt;br /&gt;
* 2.3.1.1	Community Assessment Steps	20&lt;br /&gt;
* 2.3.1.2	Methods of conducting community assessment	20&lt;br /&gt;
* 2.3.1.2.1	Comprehensive community assessment	20&lt;br /&gt;
* 2.3.1.2.2	Strategic community assessment	20&lt;br /&gt;
* 2.3.2	Pre-feasibility Study	21&lt;br /&gt;
* 2.3.3	Feasibility Study	21&lt;br /&gt;
* 2.3.3.1	Water Supply Projects Ranking and Technology Selection Criteria	22&lt;br /&gt;
* 2.3.3.1.1	Ranking of Projects	22&lt;br /&gt;
* 2.3.3.1.2	Choice of Technology	23&lt;br /&gt;
* 2.3.4	Preliminary and Detailed Design	23&lt;br /&gt;
* 2.3.4.1	Detailed Engineering Drawings	24&lt;br /&gt;
* 2.3.4.2	Detailed estimates of capital costs	24&lt;br /&gt;
* 2.3.4.3	Detailed estimates of recurrent costs	24&lt;br /&gt;
* 2.3.4.4	Anticipated revenue	25&lt;br /&gt;
* 2.3.4.5	Detailed design report	25&lt;br /&gt;
* 2.3.4.6	Project write-up to be submitted to potential financiers	25&lt;br /&gt;
* 2.3.5	Project Phasing	25&lt;br /&gt;
* 2.3.6	Procurement	26&lt;br /&gt;
* 2.3.6.1	2.2.6.1 Preparation of Tender Documents	26&lt;br /&gt;
* 2.3.6.2	Tendering process	27&lt;br /&gt;
* 2.3.7	Implementation/Construction Stage	27&lt;br /&gt;
* 2.3.7.1	Contract Management	27&lt;br /&gt;
* 2.3.7.2	Contract supervision and administration	27&lt;br /&gt;
* 2.3.8	Operation and Maintenance Stage	28&lt;br /&gt;
* 2.3.9	Performance Monitoring	28&lt;br /&gt;
* 2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans	28&lt;br /&gt;
* 2.4.1	Status of Development and Implementation of IWRMD Plans	29&lt;br /&gt;
* 2.4.2	Components of IWRMD Plans	30&lt;br /&gt;
* 2.5	Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change	30&lt;br /&gt;
* 2.6	Environmental and Social Impact Assessment Compliance	30&lt;br /&gt;
* 2.6.1	Procedures for Conducting ESIA in Tanzania	31&lt;br /&gt;
* 2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance	31&lt;br /&gt;
* 2.7	Potential Impacts of Climate Change on Water Supply Projects	32&lt;br /&gt;
* 2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages	32&lt;br /&gt;
* 2.9	References	32&lt;br /&gt;
* CHAPTER THREE	35&lt;br /&gt;
* WATER SOURCES ANALYSIS	35&lt;br /&gt;
* 3.1	Availability of Water Resources in Tanzania Mainland	35&lt;br /&gt;
* 3.2	Water Sources Available in Tanzania Mainland	38&lt;br /&gt;
* 3.2.1	Rainwater and fog harvesting	39&lt;br /&gt;
* 3.2.2	Surface Water	39&lt;br /&gt;
* 3.2.2.1	Rivers or streams	39&lt;br /&gt;
* 3.2.2.2	Impoundments	39&lt;br /&gt;
* 3.2.2.3	Springs	39&lt;br /&gt;
* 3.2.2.4	Lakes	39&lt;br /&gt;
* 3.2.2.5	Dams	40&lt;br /&gt;
* 3.2.3	Groundwater	40&lt;br /&gt;
* 3.2.3.1	Infiltration galleries/wells	40&lt;br /&gt;
* 3.2.3.2	Well	40&lt;br /&gt;
* 3.2.3.3	Classification of wells based on the aquifer tapped	41&lt;br /&gt;
* 3.2.3.3.1	Shallow wells	41&lt;br /&gt;
* 3.2.3.3.2	Deep wells	41&lt;br /&gt;
* 3.2.3.3.3	Artesian wells	41&lt;br /&gt;
* 3.3	Quality Suitability of Water Sources for Water Supply Projects	42&lt;br /&gt;
* 3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment	42&lt;br /&gt;
* 3.5	General Considerations for Selection of Water Sources	42&lt;br /&gt;
* 3.5.1	Adequacy and reliability	42&lt;br /&gt;
* 3.5.2	Quality of water sources	43&lt;br /&gt;
* 3.5.3	Technical Requirements	43&lt;br /&gt;
* 3.5.4	Cost implications to develop a water source	43&lt;br /&gt;
* 3.5.5	Protection of water sources	43&lt;br /&gt;
* 3.5.6	Legal and management requirements	44&lt;br /&gt;
* 3.5.7	Distance of water supply source	44&lt;br /&gt;
* 3.5.8	Topography of the project area and its surroundings	44&lt;br /&gt;
* 3.5.9	Elevation of a source of water supply	44&lt;br /&gt;
* 3.6	Determination of water source yield	44&lt;br /&gt;
* 3.6.1	Rainwater and fog harvesting	45&lt;br /&gt;
* 3.6.1.1	Rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.1	Types of rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.2	Components of rainwater harvesting system	46&lt;br /&gt;
* 3.6.1.1.3	Estimation of the yield	47&lt;br /&gt;
* 3.6.2	Hydrological Analysis of Surface Waters	47&lt;br /&gt;
* 3.7	Other considerations for various water sources	55&lt;br /&gt;
* 3.7.1	Water permits Considerations	55&lt;br /&gt;
* 3.7.2	Conservation of water sources	55&lt;br /&gt;
* 3.8	References	55&lt;br /&gt;
* CHAPTER FOUR	56&lt;br /&gt;
* WATER DEMAND ASSESSMENT	56&lt;br /&gt;
* 4.1	Water Demand Assessment	56&lt;br /&gt;
* 4.2	General Factors Affecting Water Demand Assessment	57&lt;br /&gt;
* 4.3	Determination of Water Demand for Different Uses	58&lt;br /&gt;
* Step 7. Establish Net Water Demand	67&lt;br /&gt;
* Step 9: Establish Operational water consumption	67&lt;br /&gt;
* Step 10: Establish System water losses	68&lt;br /&gt;
* Step 11 Establish Non-Revenue Water	69&lt;br /&gt;
* 4.4	Variations in Water Consumption	70&lt;br /&gt;
* 4.4.1	Definitions	70&lt;br /&gt;
* 4.4.2	Variation in the Rate of Consumption	71&lt;br /&gt;
* 4.4.2.1	Diurnal variation in demand	71&lt;br /&gt;
* 4.4.3	Peak Factors	72&lt;br /&gt;
* 4.4.4	Predicting Demand	74&lt;br /&gt;
* 4.4.5	Design Demand	75&lt;br /&gt;
* 4.5	References	75&lt;br /&gt;
* CHAPTER FIVE	76&lt;br /&gt;
* PIPELINES DESIGN	76&lt;br /&gt;
* 5.1	Design Requirements of pipelines	76&lt;br /&gt;
* 5.2	Types of pipelines	76&lt;br /&gt;
* 5.3	Security considerations for pipelines	76&lt;br /&gt;
* 5.3.1	Methods of water transmission and distribution	76&lt;br /&gt;
* 5.3.2	Gravity flow	77&lt;br /&gt;
* 5.3.3	Pumping with storage	77&lt;br /&gt;
* 5.3.4	Direct pumping to the distribution system	77&lt;br /&gt;
* 5.4	Pipeline Hydraulics Assessment	77&lt;br /&gt;
* 5.4.1	Pressure	77&lt;br /&gt;
* 5.4.2	Determination of Head Losses	77&lt;br /&gt;
* 5.5	Water supply transmission system	79&lt;br /&gt;
* 5.5.1	Determination of Transmission Pipe Size	79&lt;br /&gt;
* 5.5.2	Maximum Pressure	79&lt;br /&gt;
* 5.6	Distribution system	80&lt;br /&gt;
* 5.6.1	Branched System	80&lt;br /&gt;
* 5.6.2	Looped System	81&lt;br /&gt;
* 5.7	Pipe network analysis	82&lt;br /&gt;
* 5.7.1	Network analysis by Conventional method (Hardy Cross)	82&lt;br /&gt;
* 5.7.2	Network Analysis by Computer Software	82&lt;br /&gt;
* 5.7.2.1	EPANET Software	82&lt;br /&gt;
* 5.7.3	Pipeline design criteria	85&lt;br /&gt;
* 5.8	Pipeline materials selection	86&lt;br /&gt;
* 5.8.1	Considerations in Selecting Pipeline Materials	86&lt;br /&gt;
* 5.8.1.1	Flow Characteristics	86&lt;br /&gt;
* 5.8.1.2	Pipe Strength	86&lt;br /&gt;
* 5.8.1.3	Durability	87&lt;br /&gt;
* 5.8.1.4	Type of Soil	87&lt;br /&gt;
* 5.8.1.5	Availability	87&lt;br /&gt;
* 5.8.1.6	Cost of Pipes	87&lt;br /&gt;
* 5.8.2	Types of Pipe Materials Available	87&lt;br /&gt;
* 5.8.2.1	Galvanized Iron (GI) Pipes	87&lt;br /&gt;
* 5.8.2.2	Plastic Pipes	87&lt;br /&gt;
* 5.9	Appurtenances for transmission and distribution mains	88&lt;br /&gt;
* 5.9.1	Valves	89&lt;br /&gt;
* 5.9.1.1	Isolation Valves	89&lt;br /&gt;
* 5.9.1.2	Check Valves	89&lt;br /&gt;
* 5.9.1.3	Float Valves	89&lt;br /&gt;
* 5.9.1.4	Air Release Valves	89&lt;br /&gt;
* 5.9.1.5	Pressure Reducing Valves	89&lt;br /&gt;
* 5.9.1.6	Washout valves	89&lt;br /&gt;
* 5.9.2	Fittings	89&lt;br /&gt;
* 5.10	References	90&lt;br /&gt;
* CHAPTER SIX	91&lt;br /&gt;
* PUMPING SYSTEMS	91&lt;br /&gt;
* 6.1	Introduction	91&lt;br /&gt;
* 6.2	Rationale	91&lt;br /&gt;
* 6.3	Common Types of Pumps used in water supply	91&lt;br /&gt;
* 6.4	Pumping System Setup	91&lt;br /&gt;
* 6.5	Source of Pumping Power	92&lt;br /&gt;
* 6.6	Pumping system design pump selection	92&lt;br /&gt;
* 6.7	Pump Protection	95&lt;br /&gt;
* 6.8	References	95&lt;br /&gt;
* CHAPTER SEVEN	96&lt;br /&gt;
* WATER TREATMENT	96&lt;br /&gt;
* 7.1	Introduction	96&lt;br /&gt;
* 7.1.1	Classification of the qualities of water sources found in Tanzania according to the complexity of its treatment	96&lt;br /&gt;
* 7.1.2	Classification of Unit Operations to achieve water treatment levels	99&lt;br /&gt;
* 7.2	Recommended overall design approach for treatment plant components	99&lt;br /&gt;
* 7.3	Documents and websites consulted and those which are hyper-linked to the DCOM Manual	100&lt;br /&gt;
* 7.4	Water treatment design considerations	100&lt;br /&gt;
* 7.5	Water treatment levels and units	101&lt;br /&gt;
* 7.5.1	Pre-treatment	101&lt;br /&gt;
* 7.5.1.1	Scum and Floating Materials Skimmer	101&lt;br /&gt;
* 7.5.1.2	Screening or straining	101&lt;br /&gt;
* 7.5.1.3	Grit Removal	103&lt;br /&gt;
* 7.5.1.3.1	Design criteria	103&lt;br /&gt;
* 7.5.1.4	Sand Traps	105&lt;br /&gt;
* 7.5.1.5	Pre-chlorination	107&lt;br /&gt;
* 7.5.1.6	Water pre-conditioning (pH adjustment)	108&lt;br /&gt;
* 7.5.2	Primary Treatment	108&lt;br /&gt;
* 7.5.2.1	Sedimentation	108&lt;br /&gt;
* 7.5.2.2	Primary Filtration	114&lt;br /&gt;
* 7.5.2.2.1	Slow Sand Filtration	114&lt;br /&gt;
* 7.5.2.2.2	Rapid Gravity Sand Filtration	117&lt;br /&gt;
* 7.5.2.2.3	Comparison between Slow Sand Filters and Rapid Sand Filters	118&lt;br /&gt;
* 7.5.2.2.4	Other Types of Filters	119&lt;br /&gt;
* 7.5.2.3	Floatation	124&lt;br /&gt;
* 7.5.2.3.1	Dissolved-Air Floatation	124&lt;br /&gt;
* 7.5.2.3.2	Electrolytic Floatation	125&lt;br /&gt;
* 7.5.2.3.3	Dispersed-Air Floatation	125&lt;br /&gt;
* 7.5.2.4	Aeration	125&lt;br /&gt;
* 7.5.2.4.1	Falling Water Aerators	126&lt;br /&gt;
* 7.5.2.4.2	Spray Aerators	127&lt;br /&gt;
* 7.5.3	Secondary Treatment	130&lt;br /&gt;
* 7.5.3.1	Clarification	130&lt;br /&gt;
* 7.5.3.2	Coagulation	130&lt;br /&gt;
* 7.5.3.3	Flocculation	131&lt;br /&gt;
* 7.5.3.4	Filtration	131&lt;br /&gt;
* 7.5.4	Tertiary Treatment	132&lt;br /&gt;
* 7.5.4.1	Disinfection	132&lt;br /&gt;
* 7.5.4.1.1	Disinfection Methods	132&lt;br /&gt;
* 7.5.4.1.2	Chlorinators	132&lt;br /&gt;
* 7.5.4.1.3	Design considerations for chlorinators	133&lt;br /&gt;
* 7.5.4.2	Ozonation	133&lt;br /&gt;
* 7.5.4.3	Water softening	134&lt;br /&gt;
* 7.5.4.3.1	Methods of Softening	135&lt;br /&gt;
* 7.5.4.4	Defluoridation of Water	139&lt;br /&gt;
* 7.5.4.4.1	Fluorides	139&lt;br /&gt;
* 7.5.4.4.2	Defluoridation	139&lt;br /&gt;
* 7.5.4.5	Water Conditioning	141&lt;br /&gt;
* 7.5.5	Managemen&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=487</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=487"/>
		<updated>2020-03-30T18:49:18Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Header text !! Header text !! Header text&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER ONE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER TWO: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER THREE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || &lt;br /&gt;
[[CHAPTER FOUR: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER FIVE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER SIX: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER SEVEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER EIGHT: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER NINE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER TEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER ELEVEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER TWELVE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[CHAPTER THIRTEEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]] || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || [[APENDICES: APPENDICES]] || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Chapter #!! Chapter Title!! Page&lt;br /&gt;
|-&lt;br /&gt;
| i || LIST OF SPECIAL COMMITTEE MEMBERS || V&lt;br /&gt;
|-&lt;br /&gt;
| 1|| CHAPTER ONE: INTRODUCTION		 || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1|| Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.1 || Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.2 || Climate Change and Resilience to Climate Change || 2&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.3 || Public-Private Partnership in Water Supply and Sanitation Projects in Developing Countries || 3&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.4 || International Water Law || 4&lt;br /&gt;
|-&lt;br /&gt;
| 1.2 || Development Agenda and Water and Sanitation Sector in Tanzania || 5&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.1 || National Water Policy || 7&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.2|| Legal and Institutional Framework for Water Supply and Sanitation Services || 8&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.3 || Coverage and Access to Water Supply Services || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.4|| Policy Environment for Water and Sanitation Services in Tanzania || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.5 || Major Stakeholders in  Water Supply and Sanitation Projects || 10&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.6 || Water Supply and Sanitation Public Private Partnership in Tanzania || 11&lt;br /&gt;
|-&lt;br /&gt;
| 1.3 || Rationale for Preparation of the Fourth Edition DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.4 || About the Fourth Edition of the DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.5 || Organisation of the 4th edition of the DCOM Manual || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.6 || Purpose of this Volume || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.7 || References	 || 15&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
* CHAPTER TWO	17&lt;br /&gt;
* PROJECT PLANNING	17&lt;br /&gt;
* 2.1	Planning Considerations for Water Supply Projects	17&lt;br /&gt;
* 2.2	Project Planning Steps	18&lt;br /&gt;
* 2.3	Pump Protection	18&lt;br /&gt;
* 2.3.1	Initiation	18&lt;br /&gt;
* 2.3.1.1	Community Assessment Steps	20&lt;br /&gt;
* 2.3.1.2	Methods of conducting community assessment	20&lt;br /&gt;
* 2.3.1.2.1	Comprehensive community assessment	20&lt;br /&gt;
* 2.3.1.2.2	Strategic community assessment	20&lt;br /&gt;
* 2.3.2	Pre-feasibility Study	21&lt;br /&gt;
* 2.3.3	Feasibility Study	21&lt;br /&gt;
* 2.3.3.1	Water Supply Projects Ranking and Technology Selection Criteria	22&lt;br /&gt;
* 2.3.3.1.1	Ranking of Projects	22&lt;br /&gt;
* 2.3.3.1.2	Choice of Technology	23&lt;br /&gt;
* 2.3.4	Preliminary and Detailed Design	23&lt;br /&gt;
* 2.3.4.1	Detailed Engineering Drawings	24&lt;br /&gt;
* 2.3.4.2	Detailed estimates of capital costs	24&lt;br /&gt;
* 2.3.4.3	Detailed estimates of recurrent costs	24&lt;br /&gt;
* 2.3.4.4	Anticipated revenue	25&lt;br /&gt;
* 2.3.4.5	Detailed design report	25&lt;br /&gt;
* 2.3.4.6	Project write-up to be submitted to potential financiers	25&lt;br /&gt;
* 2.3.5	Project Phasing	25&lt;br /&gt;
* 2.3.6	Procurement	26&lt;br /&gt;
* 2.3.6.1	2.2.6.1 Preparation of Tender Documents	26&lt;br /&gt;
* 2.3.6.2	Tendering process	27&lt;br /&gt;
* 2.3.7	Implementation/Construction Stage	27&lt;br /&gt;
* 2.3.7.1	Contract Management	27&lt;br /&gt;
* 2.3.7.2	Contract supervision and administration	27&lt;br /&gt;
* 2.3.8	Operation and Maintenance Stage	28&lt;br /&gt;
* 2.3.9	Performance Monitoring	28&lt;br /&gt;
* 2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans	28&lt;br /&gt;
* 2.4.1	Status of Development and Implementation of IWRMD Plans	29&lt;br /&gt;
* 2.4.2	Components of IWRMD Plans	30&lt;br /&gt;
* 2.5	Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change	30&lt;br /&gt;
* 2.6	Environmental and Social Impact Assessment Compliance	30&lt;br /&gt;
* 2.6.1	Procedures for Conducting ESIA in Tanzania	31&lt;br /&gt;
* 2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance	31&lt;br /&gt;
* 2.7	Potential Impacts of Climate Change on Water Supply Projects	32&lt;br /&gt;
* 2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages	32&lt;br /&gt;
* 2.9	References	32&lt;br /&gt;
* CHAPTER THREE	35&lt;br /&gt;
* WATER SOURCES ANALYSIS	35&lt;br /&gt;
* 3.1	Availability of Water Resources in Tanzania Mainland	35&lt;br /&gt;
* 3.2	Water Sources Available in Tanzania Mainland	38&lt;br /&gt;
* 3.2.1	Rainwater and fog harvesting	39&lt;br /&gt;
* 3.2.2	Surface Water	39&lt;br /&gt;
* 3.2.2.1	Rivers or streams	39&lt;br /&gt;
* 3.2.2.2	Impoundments	39&lt;br /&gt;
* 3.2.2.3	Springs	39&lt;br /&gt;
* 3.2.2.4	Lakes	39&lt;br /&gt;
* 3.2.2.5	Dams	40&lt;br /&gt;
* 3.2.3	Groundwater	40&lt;br /&gt;
* 3.2.3.1	Infiltration galleries/wells	40&lt;br /&gt;
* 3.2.3.2	Well	40&lt;br /&gt;
* 3.2.3.3	Classification of wells based on the aquifer tapped	41&lt;br /&gt;
* 3.2.3.3.1	Shallow wells	41&lt;br /&gt;
* 3.2.3.3.2	Deep wells	41&lt;br /&gt;
* 3.2.3.3.3	Artesian wells	41&lt;br /&gt;
* 3.3	Quality Suitability of Water Sources for Water Supply Projects	42&lt;br /&gt;
* 3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment	42&lt;br /&gt;
* 3.5	General Considerations for Selection of Water Sources	42&lt;br /&gt;
* 3.5.1	Adequacy and reliability	42&lt;br /&gt;
* 3.5.2	Quality of water sources	43&lt;br /&gt;
* 3.5.3	Technical Requirements	43&lt;br /&gt;
* 3.5.4	Cost implications to develop a water source	43&lt;br /&gt;
* 3.5.5	Protection of water sources	43&lt;br /&gt;
* 3.5.6	Legal and management requirements	44&lt;br /&gt;
* 3.5.7	Distance of water supply source	44&lt;br /&gt;
* 3.5.8	Topography of the project area and its surroundings	44&lt;br /&gt;
* 3.5.9	Elevation of a source of water supply	44&lt;br /&gt;
* 3.6	Determination of water source yield	44&lt;br /&gt;
* 3.6.1	Rainwater and fog harvesting	45&lt;br /&gt;
* 3.6.1.1	Rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.1	Types of rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.2	Components of rainwater harvesting system	46&lt;br /&gt;
* 3.6.1.1.3	Estimation of the yield	47&lt;br /&gt;
* 3.6.2	Hydrological Analysis of Surface Waters	47&lt;br /&gt;
* 3.7	Other considerations for various water sources	55&lt;br /&gt;
* 3.7.1	Water permits Considerations	55&lt;br /&gt;
* 3.7.2	Conservation of water sources	55&lt;br /&gt;
* 3.8	References	55&lt;br /&gt;
* CHAPTER FOUR	56&lt;br /&gt;
* WATER DEMAND ASSESSMENT	56&lt;br /&gt;
* 4.1	Water Demand Assessment	56&lt;br /&gt;
* 4.2	General Factors Affecting Water Demand Assessment	57&lt;br /&gt;
* 4.3	Determination of Water Demand for Different Uses	58&lt;br /&gt;
* Step 7. Establish Net Water Demand	67&lt;br /&gt;
* Step 9: Establish Operational water consumption	67&lt;br /&gt;
* Step 10: Establish System water losses	68&lt;br /&gt;
* Step 11 Establish Non-Revenue Water	69&lt;br /&gt;
* 4.4	Variations in Water Consumption	70&lt;br /&gt;
* 4.4.1	Definitions	70&lt;br /&gt;
* 4.4.2	Variation in the Rate of Consumption	71&lt;br /&gt;
* 4.4.2.1	Diurnal variation in demand	71&lt;br /&gt;
* 4.4.3	Peak Factors	72&lt;br /&gt;
* 4.4.4	Predicting Demand	74&lt;br /&gt;
* 4.4.5	Design Demand	75&lt;br /&gt;
* 4.5	References	75&lt;br /&gt;
* CHAPTER FIVE	76&lt;br /&gt;
* PIPELINES DESIGN	76&lt;br /&gt;
* 5.1	Design Requirements of pipelines	76&lt;br /&gt;
* 5.2	Types of pipelines	76&lt;br /&gt;
* 5.3	Security considerations for pipelines	76&lt;br /&gt;
* 5.3.1	Methods of water transmission and distribution	76&lt;br /&gt;
* 5.3.2	Gravity flow	77&lt;br /&gt;
* 5.3.3	Pumping with storage	77&lt;br /&gt;
* 5.3.4	Direct pumping to the distribution system	77&lt;br /&gt;
* 5.4	Pipeline Hydraulics Assessment	77&lt;br /&gt;
* 5.4.1	Pressure	77&lt;br /&gt;
* 5.4.2	Determination of Head Losses	77&lt;br /&gt;
* 5.5	Water supply transmission system	79&lt;br /&gt;
* 5.5.1	Determination of Transmission Pipe Size	79&lt;br /&gt;
* 5.5.2	Maximum Pressure	79&lt;br /&gt;
* 5.6	Distribution system	80&lt;br /&gt;
* 5.6.1	Branched System	80&lt;br /&gt;
* 5.6.2	Looped System	81&lt;br /&gt;
* 5.7	Pipe network analysis	82&lt;br /&gt;
* 5.7.1	Network analysis by Conventional method (Hardy Cross)	82&lt;br /&gt;
* 5.7.2	Network Analysis by Computer Software	82&lt;br /&gt;
* 5.7.2.1	EPANET Software	82&lt;br /&gt;
* 5.7.3	Pipeline design criteria	85&lt;br /&gt;
* 5.8	Pipeline materials selection	86&lt;br /&gt;
* 5.8.1	Considerations in Selecting Pipeline Materials	86&lt;br /&gt;
* 5.8.1.1	Flow Characteristics	86&lt;br /&gt;
* 5.8.1.2	Pipe Strength	86&lt;br /&gt;
* 5.8.1.3	Durability	87&lt;br /&gt;
* 5.8.1.4	Type of Soil	87&lt;br /&gt;
* 5.8.1.5	Availability	87&lt;br /&gt;
* 5.8.1.6	Cost of Pipes	87&lt;br /&gt;
* 5.8.2	Types of Pipe Materials Available	87&lt;br /&gt;
* 5.8.2.1	Galvanized Iron (GI) Pipes	87&lt;br /&gt;
* 5.8.2.2	Plastic Pipes	87&lt;br /&gt;
* 5.9	Appurtenances for transmission and distribution mains	88&lt;br /&gt;
* 5.9.1	Valves	89&lt;br /&gt;
* 5.9.1.1	Isolation Valves	89&lt;br /&gt;
* 5.9.1.2	Check Valves	89&lt;br /&gt;
* 5.9.1.3	Float Valves	89&lt;br /&gt;
* 5.9.1.4	Air Release Valves	89&lt;br /&gt;
* 5.9.1.5	Pressure Reducing Valves	89&lt;br /&gt;
* 5.9.1.6	Washout valves	89&lt;br /&gt;
* 5.9.2	Fittings	89&lt;br /&gt;
* 5.10	References	90&lt;br /&gt;
* CHAPTER SIX	91&lt;br /&gt;
* PUMPING SYSTEMS	91&lt;br /&gt;
* 6.1	Introduction	91&lt;br /&gt;
* 6.2	Rationale	91&lt;br /&gt;
* 6.3	Common Types of Pumps used in water supply	91&lt;br /&gt;
* 6.4	Pumping System Setup	91&lt;br /&gt;
* 6.5	Source of Pumping Power	92&lt;br /&gt;
* 6.6	Pumping system design pump selection	92&lt;br /&gt;
* 6.7	Pump Protection	95&lt;br /&gt;
* 6.8	References	95&lt;br /&gt;
* CHAPTER SEVEN	96&lt;br /&gt;
* WATER TREATMENT	96&lt;br /&gt;
* 7.1	Introduction	96&lt;br /&gt;
* 7.1.1	Classification of the qualities of water sources found in Tanzania according to the complexity of its treatment	96&lt;br /&gt;
* 7.1.2	Classification of Unit Operations to achieve water treatment levels	99&lt;br /&gt;
* 7.2	Recommended overall design approach for treatment plant components	99&lt;br /&gt;
* 7.3	Documents and websites consulted and those which are hyper-linked to the DCOM Manual	100&lt;br /&gt;
* 7.4	Water treatment design considerations	100&lt;br /&gt;
* 7.5	Water treatment levels and units	101&lt;br /&gt;
* 7.5.1	Pre-treatment	101&lt;br /&gt;
* 7.5.1.1	Scum and Floating Materials Skimmer	101&lt;br /&gt;
* 7.5.1.2	Screening or straining	101&lt;br /&gt;
* 7.5.1.3	Grit Removal	103&lt;br /&gt;
* 7.5.1.3.1	Design criteria	103&lt;br /&gt;
* 7.5.1.4	Sand Traps	105&lt;br /&gt;
* 7.5.1.5	Pre-chlorination	107&lt;br /&gt;
* 7.5.1.6	Water pre-conditioning (pH adjustment)	108&lt;br /&gt;
* 7.5.2	Primary Treatment	108&lt;br /&gt;
* 7.5.2.1	Sedimentation	108&lt;br /&gt;
* 7.5.2.2	Primary Filtration	114&lt;br /&gt;
* 7.5.2.2.1	Slow Sand Filtration	114&lt;br /&gt;
* 7.5.2.2.2	Rapid Gravity Sand Filtration	117&lt;br /&gt;
* 7.5.2.2.3	Comparison between Slow Sand Filters and Rapid Sand Filters	118&lt;br /&gt;
* 7.5.2.2.4	Other Types of Filters	119&lt;br /&gt;
* 7.5.2.3	Floatation	124&lt;br /&gt;
* 7.5.2.3.1	Dissolved-Air Floatation	124&lt;br /&gt;
* 7.5.2.3.2	Electrolytic Floatation	125&lt;br /&gt;
* 7.5.2.3.3	Dispersed-Air Floatation	125&lt;br /&gt;
* 7.5.2.4	Aeration	125&lt;br /&gt;
* 7.5.2.4.1	Falling Water Aerators	126&lt;br /&gt;
* 7.5.2.4.2	Spray Aerators	127&lt;br /&gt;
* 7.5.3	Secondary Treatment	130&lt;br /&gt;
* 7.5.3.1	Clarification	130&lt;br /&gt;
* 7.5.3.2	Coagulation	130&lt;br /&gt;
* 7.5.3.3	Flocculation	131&lt;br /&gt;
* 7.5.3.4	Filtration	131&lt;br /&gt;
* 7.5.4	Tertiary Treatment	132&lt;br /&gt;
* 7.5.4.1	Disinfection	132&lt;br /&gt;
* 7.5.4.1.1	Disinfection Methods	132&lt;br /&gt;
* 7.5.4.1.2	Chlorinators	132&lt;br /&gt;
* 7.5.4.1.3	Design considerations for chlorinators	133&lt;br /&gt;
* 7.5.4.2	Ozonation	133&lt;br /&gt;
* 7.5.4.3	Water softening	134&lt;br /&gt;
* 7.5.4.3.1	Methods of Softening	135&lt;br /&gt;
* 7.5.4.4	Defluoridation of Water	139&lt;br /&gt;
* 7.5.4.4.1	Fluorides	139&lt;br /&gt;
* 7.5.4.4.2	Defluoridation	139&lt;br /&gt;
* 7.5.4.5	Water Conditioning	141&lt;br /&gt;
* 7.5.5	Managemen&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=486</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=486"/>
		<updated>2020-03-30T18:44:54Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
&lt;br /&gt;
[[CHAPTER ONE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]]&lt;br /&gt;
[[CHAPTER TWO: INTRODUCTION|CHAPTER ONE: INTRODUCTION]]&lt;br /&gt;
[[CHAPTER THREE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]]&lt;br /&gt;
[[CHAPTER FOUR: INTRODUCTION|CHAPTER ONE: INTRODUCTION]]&lt;br /&gt;
[[CHAPTER FIVE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]]&lt;br /&gt;
[[CHAPTER SIX: INTRODUCTION|CHAPTER ONE: INTRODUCTION]]&lt;br /&gt;
[[CHAPTER SEVEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]]&lt;br /&gt;
[[CHAPTER EIGHT: INTRODUCTION|CHAPTER ONE: INTRODUCTION]]&lt;br /&gt;
[[CHAPTER NINE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]]&lt;br /&gt;
[[CHAPTER TEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]]&lt;br /&gt;
[[CHAPTER ELEVEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]]&lt;br /&gt;
[[CHAPTER TWELVE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]]&lt;br /&gt;
[[CHAPTER THIRTEEN: INTRODUCTION|CHAPTER ONE: INTRODUCTION]]&lt;br /&gt;
[[APENDICES: APPENDICES]]&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Chapter #!! Chapter Title!! Page&lt;br /&gt;
|-&lt;br /&gt;
| i || LIST OF SPECIAL COMMITTEE MEMBERS || V&lt;br /&gt;
|-&lt;br /&gt;
| 1|| CHAPTER ONE: INTRODUCTION		 || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1|| Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.1 || Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.2 || Climate Change and Resilience to Climate Change || 2&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.3 || Public-Private Partnership in Water Supply and Sanitation Projects in Developing Countries || 3&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.4 || International Water Law || 4&lt;br /&gt;
|-&lt;br /&gt;
| 1.2 || Development Agenda and Water and Sanitation Sector in Tanzania || 5&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.1 || National Water Policy || 7&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.2|| Legal and Institutional Framework for Water Supply and Sanitation Services || 8&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.3 || Coverage and Access to Water Supply Services || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.4|| Policy Environment for Water and Sanitation Services in Tanzania || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.5 || Major Stakeholders in  Water Supply and Sanitation Projects || 10&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.6 || Water Supply and Sanitation Public Private Partnership in Tanzania || 11&lt;br /&gt;
|-&lt;br /&gt;
| 1.3 || Rationale for Preparation of the Fourth Edition DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.4 || About the Fourth Edition of the DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.5 || Organisation of the 4th edition of the DCOM Manual || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.6 || Purpose of this Volume || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.7 || References	 || 15&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
* CHAPTER TWO	17&lt;br /&gt;
* PROJECT PLANNING	17&lt;br /&gt;
* 2.1	Planning Considerations for Water Supply Projects	17&lt;br /&gt;
* 2.2	Project Planning Steps	18&lt;br /&gt;
* 2.3	Pump Protection	18&lt;br /&gt;
* 2.3.1	Initiation	18&lt;br /&gt;
* 2.3.1.1	Community Assessment Steps	20&lt;br /&gt;
* 2.3.1.2	Methods of conducting community assessment	20&lt;br /&gt;
* 2.3.1.2.1	Comprehensive community assessment	20&lt;br /&gt;
* 2.3.1.2.2	Strategic community assessment	20&lt;br /&gt;
* 2.3.2	Pre-feasibility Study	21&lt;br /&gt;
* 2.3.3	Feasibility Study	21&lt;br /&gt;
* 2.3.3.1	Water Supply Projects Ranking and Technology Selection Criteria	22&lt;br /&gt;
* 2.3.3.1.1	Ranking of Projects	22&lt;br /&gt;
* 2.3.3.1.2	Choice of Technology	23&lt;br /&gt;
* 2.3.4	Preliminary and Detailed Design	23&lt;br /&gt;
* 2.3.4.1	Detailed Engineering Drawings	24&lt;br /&gt;
* 2.3.4.2	Detailed estimates of capital costs	24&lt;br /&gt;
* 2.3.4.3	Detailed estimates of recurrent costs	24&lt;br /&gt;
* 2.3.4.4	Anticipated revenue	25&lt;br /&gt;
* 2.3.4.5	Detailed design report	25&lt;br /&gt;
* 2.3.4.6	Project write-up to be submitted to potential financiers	25&lt;br /&gt;
* 2.3.5	Project Phasing	25&lt;br /&gt;
* 2.3.6	Procurement	26&lt;br /&gt;
* 2.3.6.1	2.2.6.1 Preparation of Tender Documents	26&lt;br /&gt;
* 2.3.6.2	Tendering process	27&lt;br /&gt;
* 2.3.7	Implementation/Construction Stage	27&lt;br /&gt;
* 2.3.7.1	Contract Management	27&lt;br /&gt;
* 2.3.7.2	Contract supervision and administration	27&lt;br /&gt;
* 2.3.8	Operation and Maintenance Stage	28&lt;br /&gt;
* 2.3.9	Performance Monitoring	28&lt;br /&gt;
* 2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans	28&lt;br /&gt;
* 2.4.1	Status of Development and Implementation of IWRMD Plans	29&lt;br /&gt;
* 2.4.2	Components of IWRMD Plans	30&lt;br /&gt;
* 2.5	Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change	30&lt;br /&gt;
* 2.6	Environmental and Social Impact Assessment Compliance	30&lt;br /&gt;
* 2.6.1	Procedures for Conducting ESIA in Tanzania	31&lt;br /&gt;
* 2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance	31&lt;br /&gt;
* 2.7	Potential Impacts of Climate Change on Water Supply Projects	32&lt;br /&gt;
* 2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages	32&lt;br /&gt;
* 2.9	References	32&lt;br /&gt;
* CHAPTER THREE	35&lt;br /&gt;
* WATER SOURCES ANALYSIS	35&lt;br /&gt;
* 3.1	Availability of Water Resources in Tanzania Mainland	35&lt;br /&gt;
* 3.2	Water Sources Available in Tanzania Mainland	38&lt;br /&gt;
* 3.2.1	Rainwater and fog harvesting	39&lt;br /&gt;
* 3.2.2	Surface Water	39&lt;br /&gt;
* 3.2.2.1	Rivers or streams	39&lt;br /&gt;
* 3.2.2.2	Impoundments	39&lt;br /&gt;
* 3.2.2.3	Springs	39&lt;br /&gt;
* 3.2.2.4	Lakes	39&lt;br /&gt;
* 3.2.2.5	Dams	40&lt;br /&gt;
* 3.2.3	Groundwater	40&lt;br /&gt;
* 3.2.3.1	Infiltration galleries/wells	40&lt;br /&gt;
* 3.2.3.2	Well	40&lt;br /&gt;
* 3.2.3.3	Classification of wells based on the aquifer tapped	41&lt;br /&gt;
* 3.2.3.3.1	Shallow wells	41&lt;br /&gt;
* 3.2.3.3.2	Deep wells	41&lt;br /&gt;
* 3.2.3.3.3	Artesian wells	41&lt;br /&gt;
* 3.3	Quality Suitability of Water Sources for Water Supply Projects	42&lt;br /&gt;
* 3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment	42&lt;br /&gt;
* 3.5	General Considerations for Selection of Water Sources	42&lt;br /&gt;
* 3.5.1	Adequacy and reliability	42&lt;br /&gt;
* 3.5.2	Quality of water sources	43&lt;br /&gt;
* 3.5.3	Technical Requirements	43&lt;br /&gt;
* 3.5.4	Cost implications to develop a water source	43&lt;br /&gt;
* 3.5.5	Protection of water sources	43&lt;br /&gt;
* 3.5.6	Legal and management requirements	44&lt;br /&gt;
* 3.5.7	Distance of water supply source	44&lt;br /&gt;
* 3.5.8	Topography of the project area and its surroundings	44&lt;br /&gt;
* 3.5.9	Elevation of a source of water supply	44&lt;br /&gt;
* 3.6	Determination of water source yield	44&lt;br /&gt;
* 3.6.1	Rainwater and fog harvesting	45&lt;br /&gt;
* 3.6.1.1	Rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.1	Types of rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.2	Components of rainwater harvesting system	46&lt;br /&gt;
* 3.6.1.1.3	Estimation of the yield	47&lt;br /&gt;
* 3.6.2	Hydrological Analysis of Surface Waters	47&lt;br /&gt;
* 3.7	Other considerations for various water sources	55&lt;br /&gt;
* 3.7.1	Water permits Considerations	55&lt;br /&gt;
* 3.7.2	Conservation of water sources	55&lt;br /&gt;
* 3.8	References	55&lt;br /&gt;
* CHAPTER FOUR	56&lt;br /&gt;
* WATER DEMAND ASSESSMENT	56&lt;br /&gt;
* 4.1	Water Demand Assessment	56&lt;br /&gt;
* 4.2	General Factors Affecting Water Demand Assessment	57&lt;br /&gt;
* 4.3	Determination of Water Demand for Different Uses	58&lt;br /&gt;
* Step 7. Establish Net Water Demand	67&lt;br /&gt;
* Step 9: Establish Operational water consumption	67&lt;br /&gt;
* Step 10: Establish System water losses	68&lt;br /&gt;
* Step 11 Establish Non-Revenue Water	69&lt;br /&gt;
* 4.4	Variations in Water Consumption	70&lt;br /&gt;
* 4.4.1	Definitions	70&lt;br /&gt;
* 4.4.2	Variation in the Rate of Consumption	71&lt;br /&gt;
* 4.4.2.1	Diurnal variation in demand	71&lt;br /&gt;
* 4.4.3	Peak Factors	72&lt;br /&gt;
* 4.4.4	Predicting Demand	74&lt;br /&gt;
* 4.4.5	Design Demand	75&lt;br /&gt;
* 4.5	References	75&lt;br /&gt;
* CHAPTER FIVE	76&lt;br /&gt;
* PIPELINES DESIGN	76&lt;br /&gt;
* 5.1	Design Requirements of pipelines	76&lt;br /&gt;
* 5.2	Types of pipelines	76&lt;br /&gt;
* 5.3	Security considerations for pipelines	76&lt;br /&gt;
* 5.3.1	Methods of water transmission and distribution	76&lt;br /&gt;
* 5.3.2	Gravity flow	77&lt;br /&gt;
* 5.3.3	Pumping with storage	77&lt;br /&gt;
* 5.3.4	Direct pumping to the distribution system	77&lt;br /&gt;
* 5.4	Pipeline Hydraulics Assessment	77&lt;br /&gt;
* 5.4.1	Pressure	77&lt;br /&gt;
* 5.4.2	Determination of Head Losses	77&lt;br /&gt;
* 5.5	Water supply transmission system	79&lt;br /&gt;
* 5.5.1	Determination of Transmission Pipe Size	79&lt;br /&gt;
* 5.5.2	Maximum Pressure	79&lt;br /&gt;
* 5.6	Distribution system	80&lt;br /&gt;
* 5.6.1	Branched System	80&lt;br /&gt;
* 5.6.2	Looped System	81&lt;br /&gt;
* 5.7	Pipe network analysis	82&lt;br /&gt;
* 5.7.1	Network analysis by Conventional method (Hardy Cross)	82&lt;br /&gt;
* 5.7.2	Network Analysis by Computer Software	82&lt;br /&gt;
* 5.7.2.1	EPANET Software	82&lt;br /&gt;
* 5.7.3	Pipeline design criteria	85&lt;br /&gt;
* 5.8	Pipeline materials selection	86&lt;br /&gt;
* 5.8.1	Considerations in Selecting Pipeline Materials	86&lt;br /&gt;
* 5.8.1.1	Flow Characteristics	86&lt;br /&gt;
* 5.8.1.2	Pipe Strength	86&lt;br /&gt;
* 5.8.1.3	Durability	87&lt;br /&gt;
* 5.8.1.4	Type of Soil	87&lt;br /&gt;
* 5.8.1.5	Availability	87&lt;br /&gt;
* 5.8.1.6	Cost of Pipes	87&lt;br /&gt;
* 5.8.2	Types of Pipe Materials Available	87&lt;br /&gt;
* 5.8.2.1	Galvanized Iron (GI) Pipes	87&lt;br /&gt;
* 5.8.2.2	Plastic Pipes	87&lt;br /&gt;
* 5.9	Appurtenances for transmission and distribution mains	88&lt;br /&gt;
* 5.9.1	Valves	89&lt;br /&gt;
* 5.9.1.1	Isolation Valves	89&lt;br /&gt;
* 5.9.1.2	Check Valves	89&lt;br /&gt;
* 5.9.1.3	Float Valves	89&lt;br /&gt;
* 5.9.1.4	Air Release Valves	89&lt;br /&gt;
* 5.9.1.5	Pressure Reducing Valves	89&lt;br /&gt;
* 5.9.1.6	Washout valves	89&lt;br /&gt;
* 5.9.2	Fittings	89&lt;br /&gt;
* 5.10	References	90&lt;br /&gt;
* CHAPTER SIX	91&lt;br /&gt;
* PUMPING SYSTEMS	91&lt;br /&gt;
* 6.1	Introduction	91&lt;br /&gt;
* 6.2	Rationale	91&lt;br /&gt;
* 6.3	Common Types of Pumps used in water supply	91&lt;br /&gt;
* 6.4	Pumping System Setup	91&lt;br /&gt;
* 6.5	Source of Pumping Power	92&lt;br /&gt;
* 6.6	Pumping system design pump selection	92&lt;br /&gt;
* 6.7	Pump Protection	95&lt;br /&gt;
* 6.8	References	95&lt;br /&gt;
* CHAPTER SEVEN	96&lt;br /&gt;
* WATER TREATMENT	96&lt;br /&gt;
* 7.1	Introduction	96&lt;br /&gt;
* 7.1.1	Classification of the qualities of water sources found in Tanzania according to the complexity of its treatment	96&lt;br /&gt;
* 7.1.2	Classification of Unit Operations to achieve water treatment levels	99&lt;br /&gt;
* 7.2	Recommended overall design approach for treatment plant components	99&lt;br /&gt;
* 7.3	Documents and websites consulted and those which are hyper-linked to the DCOM Manual	100&lt;br /&gt;
* 7.4	Water treatment design considerations	100&lt;br /&gt;
* 7.5	Water treatment levels and units	101&lt;br /&gt;
* 7.5.1	Pre-treatment	101&lt;br /&gt;
* 7.5.1.1	Scum and Floating Materials Skimmer	101&lt;br /&gt;
* 7.5.1.2	Screening or straining	101&lt;br /&gt;
* 7.5.1.3	Grit Removal	103&lt;br /&gt;
* 7.5.1.3.1	Design criteria	103&lt;br /&gt;
* 7.5.1.4	Sand Traps	105&lt;br /&gt;
* 7.5.1.5	Pre-chlorination	107&lt;br /&gt;
* 7.5.1.6	Water pre-conditioning (pH adjustment)	108&lt;br /&gt;
* 7.5.2	Primary Treatment	108&lt;br /&gt;
* 7.5.2.1	Sedimentation	108&lt;br /&gt;
* 7.5.2.2	Primary Filtration	114&lt;br /&gt;
* 7.5.2.2.1	Slow Sand Filtration	114&lt;br /&gt;
* 7.5.2.2.2	Rapid Gravity Sand Filtration	117&lt;br /&gt;
* 7.5.2.2.3	Comparison between Slow Sand Filters and Rapid Sand Filters	118&lt;br /&gt;
* 7.5.2.2.4	Other Types of Filters	119&lt;br /&gt;
* 7.5.2.3	Floatation	124&lt;br /&gt;
* 7.5.2.3.1	Dissolved-Air Floatation	124&lt;br /&gt;
* 7.5.2.3.2	Electrolytic Floatation	125&lt;br /&gt;
* 7.5.2.3.3	Dispersed-Air Floatation	125&lt;br /&gt;
* 7.5.2.4	Aeration	125&lt;br /&gt;
* 7.5.2.4.1	Falling Water Aerators	126&lt;br /&gt;
* 7.5.2.4.2	Spray Aerators	127&lt;br /&gt;
* 7.5.3	Secondary Treatment	130&lt;br /&gt;
* 7.5.3.1	Clarification	130&lt;br /&gt;
* 7.5.3.2	Coagulation	130&lt;br /&gt;
* 7.5.3.3	Flocculation	131&lt;br /&gt;
* 7.5.3.4	Filtration	131&lt;br /&gt;
* 7.5.4	Tertiary Treatment	132&lt;br /&gt;
* 7.5.4.1	Disinfection	132&lt;br /&gt;
* 7.5.4.1.1	Disinfection Methods	132&lt;br /&gt;
* 7.5.4.1.2	Chlorinators	132&lt;br /&gt;
* 7.5.4.1.3	Design considerations for chlorinators	133&lt;br /&gt;
* 7.5.4.2	Ozonation	133&lt;br /&gt;
* 7.5.4.3	Water softening	134&lt;br /&gt;
* 7.5.4.3.1	Methods of Softening	135&lt;br /&gt;
* 7.5.4.4	Defluoridation of Water	139&lt;br /&gt;
* 7.5.4.4.1	Fluorides	139&lt;br /&gt;
* 7.5.4.4.2	Defluoridation	139&lt;br /&gt;
* 7.5.4.5	Water Conditioning	141&lt;br /&gt;
* 7.5.5	Managemen&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=485</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=485"/>
		<updated>2020-03-30T18:41:24Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
&lt;br /&gt;
[[CHAPTER ONE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]]&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Chapter #!! Chapter Title!! Page&lt;br /&gt;
|-&lt;br /&gt;
| i || LIST OF SPECIAL COMMITTEE MEMBERS || V&lt;br /&gt;
|-&lt;br /&gt;
| 1|| CHAPTER ONE: INTRODUCTION		 || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1|| Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.1 || Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.2 || Climate Change and Resilience to Climate Change || 2&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.3 || Public-Private Partnership in Water Supply and Sanitation Projects in Developing Countries || 3&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.4 || International Water Law || 4&lt;br /&gt;
|-&lt;br /&gt;
| 1.2 || Development Agenda and Water and Sanitation Sector in Tanzania || 5&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.1 || National Water Policy || 7&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.2|| Legal and Institutional Framework for Water Supply and Sanitation Services || 8&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.3 || Coverage and Access to Water Supply Services || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.4|| Policy Environment for Water and Sanitation Services in Tanzania || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.5 || Major Stakeholders in  Water Supply and Sanitation Projects || 10&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.6 || Water Supply and Sanitation Public Private Partnership in Tanzania || 11&lt;br /&gt;
|-&lt;br /&gt;
| 1.3 || Rationale for Preparation of the Fourth Edition DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.4 || About the Fourth Edition of the DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.5 || Organisation of the 4th edition of the DCOM Manual || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.6 || Purpose of this Volume || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.7 || References	 || 15&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
* CHAPTER TWO	17&lt;br /&gt;
* PROJECT PLANNING	17&lt;br /&gt;
* 2.1	Planning Considerations for Water Supply Projects	17&lt;br /&gt;
* 2.2	Project Planning Steps	18&lt;br /&gt;
* 2.3	Pump Protection	18&lt;br /&gt;
* 2.3.1	Initiation	18&lt;br /&gt;
* 2.3.1.1	Community Assessment Steps	20&lt;br /&gt;
* 2.3.1.2	Methods of conducting community assessment	20&lt;br /&gt;
* 2.3.1.2.1	Comprehensive community assessment	20&lt;br /&gt;
* 2.3.1.2.2	Strategic community assessment	20&lt;br /&gt;
* 2.3.2	Pre-feasibility Study	21&lt;br /&gt;
* 2.3.3	Feasibility Study	21&lt;br /&gt;
* 2.3.3.1	Water Supply Projects Ranking and Technology Selection Criteria	22&lt;br /&gt;
* 2.3.3.1.1	Ranking of Projects	22&lt;br /&gt;
* 2.3.3.1.2	Choice of Technology	23&lt;br /&gt;
* 2.3.4	Preliminary and Detailed Design	23&lt;br /&gt;
* 2.3.4.1	Detailed Engineering Drawings	24&lt;br /&gt;
* 2.3.4.2	Detailed estimates of capital costs	24&lt;br /&gt;
* 2.3.4.3	Detailed estimates of recurrent costs	24&lt;br /&gt;
* 2.3.4.4	Anticipated revenue	25&lt;br /&gt;
* 2.3.4.5	Detailed design report	25&lt;br /&gt;
* 2.3.4.6	Project write-up to be submitted to potential financiers	25&lt;br /&gt;
* 2.3.5	Project Phasing	25&lt;br /&gt;
* 2.3.6	Procurement	26&lt;br /&gt;
* 2.3.6.1	2.2.6.1 Preparation of Tender Documents	26&lt;br /&gt;
* 2.3.6.2	Tendering process	27&lt;br /&gt;
* 2.3.7	Implementation/Construction Stage	27&lt;br /&gt;
* 2.3.7.1	Contract Management	27&lt;br /&gt;
* 2.3.7.2	Contract supervision and administration	27&lt;br /&gt;
* 2.3.8	Operation and Maintenance Stage	28&lt;br /&gt;
* 2.3.9	Performance Monitoring	28&lt;br /&gt;
* 2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans	28&lt;br /&gt;
* 2.4.1	Status of Development and Implementation of IWRMD Plans	29&lt;br /&gt;
* 2.4.2	Components of IWRMD Plans	30&lt;br /&gt;
* 2.5	Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change	30&lt;br /&gt;
* 2.6	Environmental and Social Impact Assessment Compliance	30&lt;br /&gt;
* 2.6.1	Procedures for Conducting ESIA in Tanzania	31&lt;br /&gt;
* 2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance	31&lt;br /&gt;
* 2.7	Potential Impacts of Climate Change on Water Supply Projects	32&lt;br /&gt;
* 2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages	32&lt;br /&gt;
* 2.9	References	32&lt;br /&gt;
* CHAPTER THREE	35&lt;br /&gt;
* WATER SOURCES ANALYSIS	35&lt;br /&gt;
* 3.1	Availability of Water Resources in Tanzania Mainland	35&lt;br /&gt;
* 3.2	Water Sources Available in Tanzania Mainland	38&lt;br /&gt;
* 3.2.1	Rainwater and fog harvesting	39&lt;br /&gt;
* 3.2.2	Surface Water	39&lt;br /&gt;
* 3.2.2.1	Rivers or streams	39&lt;br /&gt;
* 3.2.2.2	Impoundments	39&lt;br /&gt;
* 3.2.2.3	Springs	39&lt;br /&gt;
* 3.2.2.4	Lakes	39&lt;br /&gt;
* 3.2.2.5	Dams	40&lt;br /&gt;
* 3.2.3	Groundwater	40&lt;br /&gt;
* 3.2.3.1	Infiltration galleries/wells	40&lt;br /&gt;
* 3.2.3.2	Well	40&lt;br /&gt;
* 3.2.3.3	Classification of wells based on the aquifer tapped	41&lt;br /&gt;
* 3.2.3.3.1	Shallow wells	41&lt;br /&gt;
* 3.2.3.3.2	Deep wells	41&lt;br /&gt;
* 3.2.3.3.3	Artesian wells	41&lt;br /&gt;
* 3.3	Quality Suitability of Water Sources for Water Supply Projects	42&lt;br /&gt;
* 3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment	42&lt;br /&gt;
* 3.5	General Considerations for Selection of Water Sources	42&lt;br /&gt;
* 3.5.1	Adequacy and reliability	42&lt;br /&gt;
* 3.5.2	Quality of water sources	43&lt;br /&gt;
* 3.5.3	Technical Requirements	43&lt;br /&gt;
* 3.5.4	Cost implications to develop a water source	43&lt;br /&gt;
* 3.5.5	Protection of water sources	43&lt;br /&gt;
* 3.5.6	Legal and management requirements	44&lt;br /&gt;
* 3.5.7	Distance of water supply source	44&lt;br /&gt;
* 3.5.8	Topography of the project area and its surroundings	44&lt;br /&gt;
* 3.5.9	Elevation of a source of water supply	44&lt;br /&gt;
* 3.6	Determination of water source yield	44&lt;br /&gt;
* 3.6.1	Rainwater and fog harvesting	45&lt;br /&gt;
* 3.6.1.1	Rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.1	Types of rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.2	Components of rainwater harvesting system	46&lt;br /&gt;
* 3.6.1.1.3	Estimation of the yield	47&lt;br /&gt;
* 3.6.2	Hydrological Analysis of Surface Waters	47&lt;br /&gt;
* 3.7	Other considerations for various water sources	55&lt;br /&gt;
* 3.7.1	Water permits Considerations	55&lt;br /&gt;
* 3.7.2	Conservation of water sources	55&lt;br /&gt;
* 3.8	References	55&lt;br /&gt;
* CHAPTER FOUR	56&lt;br /&gt;
* WATER DEMAND ASSESSMENT	56&lt;br /&gt;
* 4.1	Water Demand Assessment	56&lt;br /&gt;
* 4.2	General Factors Affecting Water Demand Assessment	57&lt;br /&gt;
* 4.3	Determination of Water Demand for Different Uses	58&lt;br /&gt;
* Step 7. Establish Net Water Demand	67&lt;br /&gt;
* Step 9: Establish Operational water consumption	67&lt;br /&gt;
* Step 10: Establish System water losses	68&lt;br /&gt;
* Step 11 Establish Non-Revenue Water	69&lt;br /&gt;
* 4.4	Variations in Water Consumption	70&lt;br /&gt;
* 4.4.1	Definitions	70&lt;br /&gt;
* 4.4.2	Variation in the Rate of Consumption	71&lt;br /&gt;
* 4.4.2.1	Diurnal variation in demand	71&lt;br /&gt;
* 4.4.3	Peak Factors	72&lt;br /&gt;
* 4.4.4	Predicting Demand	74&lt;br /&gt;
* 4.4.5	Design Demand	75&lt;br /&gt;
* 4.5	References	75&lt;br /&gt;
* CHAPTER FIVE	76&lt;br /&gt;
* PIPELINES DESIGN	76&lt;br /&gt;
* 5.1	Design Requirements of pipelines	76&lt;br /&gt;
* 5.2	Types of pipelines	76&lt;br /&gt;
* 5.3	Security considerations for pipelines	76&lt;br /&gt;
* 5.3.1	Methods of water transmission and distribution	76&lt;br /&gt;
* 5.3.2	Gravity flow	77&lt;br /&gt;
* 5.3.3	Pumping with storage	77&lt;br /&gt;
* 5.3.4	Direct pumping to the distribution system	77&lt;br /&gt;
* 5.4	Pipeline Hydraulics Assessment	77&lt;br /&gt;
* 5.4.1	Pressure	77&lt;br /&gt;
* 5.4.2	Determination of Head Losses	77&lt;br /&gt;
* 5.5	Water supply transmission system	79&lt;br /&gt;
* 5.5.1	Determination of Transmission Pipe Size	79&lt;br /&gt;
* 5.5.2	Maximum Pressure	79&lt;br /&gt;
* 5.6	Distribution system	80&lt;br /&gt;
* 5.6.1	Branched System	80&lt;br /&gt;
* 5.6.2	Looped System	81&lt;br /&gt;
* 5.7	Pipe network analysis	82&lt;br /&gt;
* 5.7.1	Network analysis by Conventional method (Hardy Cross)	82&lt;br /&gt;
* 5.7.2	Network Analysis by Computer Software	82&lt;br /&gt;
* 5.7.2.1	EPANET Software	82&lt;br /&gt;
* 5.7.3	Pipeline design criteria	85&lt;br /&gt;
* 5.8	Pipeline materials selection	86&lt;br /&gt;
* 5.8.1	Considerations in Selecting Pipeline Materials	86&lt;br /&gt;
* 5.8.1.1	Flow Characteristics	86&lt;br /&gt;
* 5.8.1.2	Pipe Strength	86&lt;br /&gt;
* 5.8.1.3	Durability	87&lt;br /&gt;
* 5.8.1.4	Type of Soil	87&lt;br /&gt;
* 5.8.1.5	Availability	87&lt;br /&gt;
* 5.8.1.6	Cost of Pipes	87&lt;br /&gt;
* 5.8.2	Types of Pipe Materials Available	87&lt;br /&gt;
* 5.8.2.1	Galvanized Iron (GI) Pipes	87&lt;br /&gt;
* 5.8.2.2	Plastic Pipes	87&lt;br /&gt;
* 5.9	Appurtenances for transmission and distribution mains	88&lt;br /&gt;
* 5.9.1	Valves	89&lt;br /&gt;
* 5.9.1.1	Isolation Valves	89&lt;br /&gt;
* 5.9.1.2	Check Valves	89&lt;br /&gt;
* 5.9.1.3	Float Valves	89&lt;br /&gt;
* 5.9.1.4	Air Release Valves	89&lt;br /&gt;
* 5.9.1.5	Pressure Reducing Valves	89&lt;br /&gt;
* 5.9.1.6	Washout valves	89&lt;br /&gt;
* 5.9.2	Fittings	89&lt;br /&gt;
* 5.10	References	90&lt;br /&gt;
* CHAPTER SIX	91&lt;br /&gt;
* PUMPING SYSTEMS	91&lt;br /&gt;
* 6.1	Introduction	91&lt;br /&gt;
* 6.2	Rationale	91&lt;br /&gt;
* 6.3	Common Types of Pumps used in water supply	91&lt;br /&gt;
* 6.4	Pumping System Setup	91&lt;br /&gt;
* 6.5	Source of Pumping Power	92&lt;br /&gt;
* 6.6	Pumping system design pump selection	92&lt;br /&gt;
* 6.7	Pump Protection	95&lt;br /&gt;
* 6.8	References	95&lt;br /&gt;
* CHAPTER SEVEN	96&lt;br /&gt;
* WATER TREATMENT	96&lt;br /&gt;
* 7.1	Introduction	96&lt;br /&gt;
* 7.1.1	Classification of the qualities of water sources found in Tanzania according to the complexity of its treatment	96&lt;br /&gt;
* 7.1.2	Classification of Unit Operations to achieve water treatment levels	99&lt;br /&gt;
* 7.2	Recommended overall design approach for treatment plant components	99&lt;br /&gt;
* 7.3	Documents and websites consulted and those which are hyper-linked to the DCOM Manual	100&lt;br /&gt;
* 7.4	Water treatment design considerations	100&lt;br /&gt;
* 7.5	Water treatment levels and units	101&lt;br /&gt;
* 7.5.1	Pre-treatment	101&lt;br /&gt;
* 7.5.1.1	Scum and Floating Materials Skimmer	101&lt;br /&gt;
* 7.5.1.2	Screening or straining	101&lt;br /&gt;
* 7.5.1.3	Grit Removal	103&lt;br /&gt;
* 7.5.1.3.1	Design criteria	103&lt;br /&gt;
* 7.5.1.4	Sand Traps	105&lt;br /&gt;
* 7.5.1.5	Pre-chlorination	107&lt;br /&gt;
* 7.5.1.6	Water pre-conditioning (pH adjustment)	108&lt;br /&gt;
* 7.5.2	Primary Treatment	108&lt;br /&gt;
* 7.5.2.1	Sedimentation	108&lt;br /&gt;
* 7.5.2.2	Primary Filtration	114&lt;br /&gt;
* 7.5.2.2.1	Slow Sand Filtration	114&lt;br /&gt;
* 7.5.2.2.2	Rapid Gravity Sand Filtration	117&lt;br /&gt;
* 7.5.2.2.3	Comparison between Slow Sand Filters and Rapid Sand Filters	118&lt;br /&gt;
* 7.5.2.2.4	Other Types of Filters	119&lt;br /&gt;
* 7.5.2.3	Floatation	124&lt;br /&gt;
* 7.5.2.3.1	Dissolved-Air Floatation	124&lt;br /&gt;
* 7.5.2.3.2	Electrolytic Floatation	125&lt;br /&gt;
* 7.5.2.3.3	Dispersed-Air Floatation	125&lt;br /&gt;
* 7.5.2.4	Aeration	125&lt;br /&gt;
* 7.5.2.4.1	Falling Water Aerators	126&lt;br /&gt;
* 7.5.2.4.2	Spray Aerators	127&lt;br /&gt;
* 7.5.3	Secondary Treatment	130&lt;br /&gt;
* 7.5.3.1	Clarification	130&lt;br /&gt;
* 7.5.3.2	Coagulation	130&lt;br /&gt;
* 7.5.3.3	Flocculation	131&lt;br /&gt;
* 7.5.3.4	Filtration	131&lt;br /&gt;
* 7.5.4	Tertiary Treatment	132&lt;br /&gt;
* 7.5.4.1	Disinfection	132&lt;br /&gt;
* 7.5.4.1.1	Disinfection Methods	132&lt;br /&gt;
* 7.5.4.1.2	Chlorinators	132&lt;br /&gt;
* 7.5.4.1.3	Design considerations for chlorinators	133&lt;br /&gt;
* 7.5.4.2	Ozonation	133&lt;br /&gt;
* 7.5.4.3	Water softening	134&lt;br /&gt;
* 7.5.4.3.1	Methods of Softening	135&lt;br /&gt;
* 7.5.4.4	Defluoridation of Water	139&lt;br /&gt;
* 7.5.4.4.1	Fluorides	139&lt;br /&gt;
* 7.5.4.4.2	Defluoridation	139&lt;br /&gt;
* 7.5.4.5	Water Conditioning	141&lt;br /&gt;
* 7.5.5	Management of Water Treatment Sludge	141&lt;br /&gt;
* 7.5.5.1	Treatment of Water Treatment Sludge	141&lt;br /&gt;
* 7.5.5.1.1	Sludge Thickening	141&lt;br /&gt;
* 7.5.5.1.2	Sludge Dewatering	143&lt;br /&gt;
* 7.5.5.1.3	Sludge Drying Beds	144&lt;br /&gt;
* 7.5.5.1.4	Sludge Lagoons	144&lt;br /&gt;
* 7.5.5.1.5	Mechanical Sludge Dewatering	145&lt;br /&gt;
* 7.5.5.1.6	Backwash Water Recovery	145&lt;br /&gt;
* 7.5.5.1.7	Waste from Slow Sand Filters	146&lt;br /&gt;
* 7.5.5.2	Disposal of sludge	147&lt;br /&gt;
* 7.6	References	147&lt;br /&gt;
* CHAPTER EIGHT	148&lt;br /&gt;
* TREATMENT OF WATERS WITH SPECIAL CONTAMINANTS	148&lt;br /&gt;
* 8.1	Natural Organic Matter	148&lt;br /&gt;
* 8.2	Arsenic	149&lt;br /&gt;
* 8.3	Radioactive	149&lt;br /&gt;
* 8.4	Fluoride removal from drinking water	149&lt;br /&gt;
* 8.5	Toxic Cyanobacteria in Drinking Water	150&lt;br /&gt;
* 8.6	Available methods for removal of special water contaminants	152&lt;br /&gt;
* 8.7	Desalination	152&lt;br /&gt;
* 8.7.1	Additive method	152&lt;br /&gt;
* 8.7.2	Adsorption methods	153&lt;br /&gt;
* 8.7.3	Capacitive deionization (CDI)	153&lt;br /&gt;
* 8.7.4	Membrane Filtration	154&lt;br /&gt;
* 8.7.5	Reverse Osmosis	156&lt;br /&gt;
* 8.8	References	158&lt;br /&gt;
* CHAPTER NINE	159&lt;br /&gt;
* DESIGN OF WATER STRUCTURES	159&lt;br /&gt;
* 9.1	Sizing and Locating Water Structures	159&lt;br /&gt;
* 9.1.1	Tanks	159&lt;br /&gt;
* 9.1.1.1	Storage tanks	159&lt;br /&gt;
* 9.1.1.2	Sedimentation/Settling Tanks	160&lt;br /&gt;
* 9.1.1.3	Break Pressure Tanks	161&lt;br /&gt;
* 9.1.2	Water Intakes	162&lt;br /&gt;
* 9.1.3	Dams	164&lt;br /&gt;
* 9.1.3.1	Engineering Classification of Dams	164&lt;br /&gt;
* 9.1.3.2	Size classification of dams	164&lt;br /&gt;
* 9.1.3.3	Feasibility and geotechnical investigations	166&lt;br /&gt;
* 9.1.3.4	Hydrological analysis of the catchment	167&lt;br /&gt;
* 9.1.4	Geotechnical Investigation	169&lt;br /&gt;
* 9.1.4.1	Design of dams	170&lt;br /&gt;
* 9.1.5	Boreholes	173&lt;br /&gt;
* 9.1.5.1	Groundwater prospecting	179&lt;br /&gt;
* 9.1.5.2	Drilling	182&lt;br /&gt;
* 9.1.5.3	Siting of Well/Borehole	182&lt;br /&gt;
* 9.1.5.4	Well design	183&lt;br /&gt;
* 9.1.5.5	Pumping Tests	183&lt;br /&gt;
* 9.1.5.6	Groundwater quality	187&lt;br /&gt;
* 9.1.6	Water points and Service connections	190&lt;br /&gt;
* 9.1.7	Common Types of Water Points	191&lt;br /&gt;
* 9.1.8	Minimum Technical Requirements of Water Points	191&lt;br /&gt;
* 9.1.9	Criteria  for Design of Water Point/Kiosks	191&lt;br /&gt;
* 9.1.10	Location Considerations for Water Points	192&lt;br /&gt;
* 9.1.11	Technical Tips to Improve Water Points	193&lt;br /&gt;
* 9.1.11.1	Rainwater harvesting	196&lt;br /&gt;
* 9.1.11.2	Fog harvesting	200&lt;br /&gt;
* 9.2	Structural Design of Concrete	201&lt;br /&gt;
* 9.2.1	Structural requirements	201&lt;br /&gt;
* 9.2.2	Methods	201&lt;br /&gt;
* 9.2.2.1	Working Stress Method	201&lt;br /&gt;
* 9.2.2.2	Ultimate Load Method	201&lt;br /&gt;
* 9.2.2.3	Limit State Method	201&lt;br /&gt;
* 9.3	References	201&lt;br /&gt;
* CHAPTER TEN	203&lt;br /&gt;
* APPLICATION SOFTWARE	203&lt;br /&gt;
* 10.1	Application Software Contexts	203&lt;br /&gt;
* 10.2	Recommended Application Software	203&lt;br /&gt;
* 10.2.1	Distribution Network Design Software	203&lt;br /&gt;
* 10.2.1.1	Epanet	203&lt;br /&gt;
* 10.2.1.2	AutoCAD	204&lt;br /&gt;
* 10.2.1.3	WaterCAD	204&lt;br /&gt;
* 10.2.1.4	WaterGEMS	204&lt;br /&gt;
* 10.2.1.5	KY PIPES	204&lt;br /&gt;
* 10.2.1.6	GeoNode	204&lt;br /&gt;
* 10.2.1.7	AutoStudio	204&lt;br /&gt;
* 10.2.1.8	InfoWater	205&lt;br /&gt;
* 10.2.1.9	GIS Software	205&lt;br /&gt;
* 10.2.1.10	MS Project	205&lt;br /&gt;
* 10.2.2	Operation and Maintenance Software	205&lt;br /&gt;
* 10.2.2.1	MS Project	205&lt;br /&gt;
* 10.2.2.2	Excel	205&lt;br /&gt;
* 10.2.2.3	EDAMS	206&lt;br /&gt;
* 10.2.3	Water Quality	206&lt;br /&gt;
* 10.2.3.1	WaterCAD	206&lt;br /&gt;
* 10.3	Supervisory, Control and Data Acquisition (SCADA) Systems	206&lt;br /&gt;
* 10.4	References	207&lt;br /&gt;
* CHAPTER ELEVEN	208&lt;br /&gt;
* METERING	208&lt;br /&gt;
* 11.1	Introduction	208&lt;br /&gt;
* 11.2	Types of Water Meters	208&lt;br /&gt;
* 11.3	Prepaid Meters	208&lt;br /&gt;
* 11.4	Types of Prepaid water models commonly used in Tanzania	209&lt;br /&gt;
* 11.5	Importance of Prepaid Water Metering	210&lt;br /&gt;
* 11.6	Design Considerations for Prepaid Water Meters	210&lt;br /&gt;
* 11.7	Design considerations for prepaid public standpipes	211&lt;br /&gt;
* 11.8	Design consideration for individual domestic customer	212&lt;br /&gt;
* 11.9	Design consideration for Commercial and Institutional Customers	212&lt;br /&gt;
* 11.10	Importance of integrating Prepaid with Post paid revenue management	212&lt;br /&gt;
* 11.11	Selection Criteria for Prepaid water meters	212&lt;br /&gt;
* 11.12	References	214&lt;br /&gt;
* 11.13	Internet Links:	216&lt;br /&gt;
* CHAPTER TWELVE	217&lt;br /&gt;
* DESIGN STANDARDS AND SPECIFICATIONS	217&lt;br /&gt;
* 12.1	Design Standards	217&lt;br /&gt;
* 12.2	Specifications	218&lt;br /&gt;
* 12.3	Materials	218&lt;br /&gt;
* 12.3.1	Building Materials	218&lt;br /&gt;
* 12.3.2	Materials Testing	219&lt;br /&gt;
* 12.3.2.1	Aggregates	219&lt;br /&gt;
* 12.3.2.2	Water	221&lt;br /&gt;
* 12.3.2.3	Cement	221&lt;br /&gt;
* 12.3.2.4	Concrete Works	221&lt;br /&gt;
* 12.3.2.5	Steel	222&lt;br /&gt;
* 12.4	Soil Test	222&lt;br /&gt;
* 12.4.1	Methodology of conducting Soil Investigation for borehole and test pit	222&lt;br /&gt;
* 12.4.2	Soil Investigation for dams	223&lt;br /&gt;
* 12.4.3	Suitability of soil materials for dam construction	223&lt;br /&gt;
* 12.4.4	Determination of In-Situ Bearing Capacity of the Soil	224&lt;br /&gt;
* 12.5	References:	227&lt;br /&gt;
* CHAPTER THIRTEEN	228&lt;br /&gt;
* ROLE OF STAKEHOLDERS IN DESIGN OF WATER SUPPLY PROJECTS	228&lt;br /&gt;
* 13.1	Types of Stakeholders	228&lt;br /&gt;
* 13.2	Roles of stakeholders	228&lt;br /&gt;
* 13.3	References	230&lt;br /&gt;
* APPENDIX A: CLIMATE CHANGE AND RESILIENCE TO CLIMATE CHANGE	232&lt;br /&gt;
* APPENDIX B: MINIMUM WATER FLOW REQUIREMENT FOR FIRE FIGHTING	237&lt;br /&gt;
* APPENDIX C: EXAMPLE: ESTIMATING THE CAPACITY OF TANK	239&lt;br /&gt;
* APPENDIX D: STRUCTURAL DESIGN OF CONCRETE	241&lt;br /&gt;
* APPENDIX E: SUPPLY PUMPING SYSTEMS	251&lt;br /&gt;
* APPENDIX F: SOURCE OF PUMPING POWER	263&lt;br /&gt;
* APPENDIX G: ADDITIONAL DETAILS OF VARIOUS UNIT OPRATIONS	275&lt;br /&gt;
* APPENDIX H: METHODS FOR DISINFECTING WATER	281&lt;br /&gt;
* APPENDIX I: MEASUREMENTS OF WATER HARDNESS	287&lt;br /&gt;
* APPENDIX J: BASIC STATISTICS USED IN ESTIMATION OF DESIGN OF FLOOD EVENTS	289&lt;br /&gt;
* APPENDIX K: DAMS DETAIL DESIGN	294&lt;br /&gt;
* APPENDIX L: STANDARD DRAWINGS	306&lt;br /&gt;
* APPENDIX M: SELECTED INTAKE DESIGNS.	307&lt;br /&gt;
* SUBJECT INDEX	309&lt;br /&gt;
*&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
	<entry>
		<id>http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=484</id>
		<title>DCOM Volume I</title>
		<link rel="alternate" type="text/html" href="http://design.maji.go.tz/index.php?title=DCOM_Volume_I&amp;diff=484"/>
		<updated>2020-03-30T18:41:04Z</updated>

		<summary type="html">&lt;p&gt;Jlungo: &lt;/p&gt;
&lt;hr /&gt;
&lt;div&gt;[[Image:DCOM_Volume_I_2020-03-11.png|540px|link=Preface]]&lt;br /&gt;
&amp;lt;h4&amp;gt;Volume I: Design of Water Supply Projects &amp;lt;/h4&amp;gt; [[Preface|Readmore...]]or Download  [[:File:DCOM_Volume_I_2020-03-10.pdf| Volume I PDF]]&lt;br /&gt;
&lt;br /&gt;
TABLE OF CONTENTS&lt;br /&gt;
&lt;br /&gt;
[CHAPTER ONE: INTRODUCTION|CHAPTER ONE: INTRODUCTION]&lt;br /&gt;
{| class=&amp;quot;wikitable&amp;quot;&lt;br /&gt;
|-&lt;br /&gt;
! Chapter #!! Chapter Title!! Page&lt;br /&gt;
|-&lt;br /&gt;
| i || LIST OF SPECIAL COMMITTEE MEMBERS || V&lt;br /&gt;
|-&lt;br /&gt;
| 1|| CHAPTER ONE: INTRODUCTION		 || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1|| Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.1 || Global Considerations on Water Supply and Sanitation || 1&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.2 || Climate Change and Resilience to Climate Change || 2&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.3 || Public-Private Partnership in Water Supply and Sanitation Projects in Developing Countries || 3&lt;br /&gt;
|-&lt;br /&gt;
| 1.1.4 || International Water Law || 4&lt;br /&gt;
|-&lt;br /&gt;
| 1.2 || Development Agenda and Water and Sanitation Sector in Tanzania || 5&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.1 || National Water Policy || 7&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.2|| Legal and Institutional Framework for Water Supply and Sanitation Services || 8&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.3 || Coverage and Access to Water Supply Services || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.4|| Policy Environment for Water and Sanitation Services in Tanzania || 9&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.5 || Major Stakeholders in  Water Supply and Sanitation Projects || 10&lt;br /&gt;
|-&lt;br /&gt;
| 1.2.6 || Water Supply and Sanitation Public Private Partnership in Tanzania || 11&lt;br /&gt;
|-&lt;br /&gt;
| 1.3 || Rationale for Preparation of the Fourth Edition DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.4 || About the Fourth Edition of the DCOM Manual || 13&lt;br /&gt;
|-&lt;br /&gt;
| 1.5 || Organisation of the 4th edition of the DCOM Manual || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.6 || Purpose of this Volume || 14&lt;br /&gt;
|-&lt;br /&gt;
| 1.7 || References	 || 15&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|-&lt;br /&gt;
| Example || Example || Example&lt;br /&gt;
|}&lt;br /&gt;
&lt;br /&gt;
&lt;br /&gt;
* CHAPTER TWO	17&lt;br /&gt;
* PROJECT PLANNING	17&lt;br /&gt;
* 2.1	Planning Considerations for Water Supply Projects	17&lt;br /&gt;
* 2.2	Project Planning Steps	18&lt;br /&gt;
* 2.3	Pump Protection	18&lt;br /&gt;
* 2.3.1	Initiation	18&lt;br /&gt;
* 2.3.1.1	Community Assessment Steps	20&lt;br /&gt;
* 2.3.1.2	Methods of conducting community assessment	20&lt;br /&gt;
* 2.3.1.2.1	Comprehensive community assessment	20&lt;br /&gt;
* 2.3.1.2.2	Strategic community assessment	20&lt;br /&gt;
* 2.3.2	Pre-feasibility Study	21&lt;br /&gt;
* 2.3.3	Feasibility Study	21&lt;br /&gt;
* 2.3.3.1	Water Supply Projects Ranking and Technology Selection Criteria	22&lt;br /&gt;
* 2.3.3.1.1	Ranking of Projects	22&lt;br /&gt;
* 2.3.3.1.2	Choice of Technology	23&lt;br /&gt;
* 2.3.4	Preliminary and Detailed Design	23&lt;br /&gt;
* 2.3.4.1	Detailed Engineering Drawings	24&lt;br /&gt;
* 2.3.4.2	Detailed estimates of capital costs	24&lt;br /&gt;
* 2.3.4.3	Detailed estimates of recurrent costs	24&lt;br /&gt;
* 2.3.4.4	Anticipated revenue	25&lt;br /&gt;
* 2.3.4.5	Detailed design report	25&lt;br /&gt;
* 2.3.4.6	Project write-up to be submitted to potential financiers	25&lt;br /&gt;
* 2.3.5	Project Phasing	25&lt;br /&gt;
* 2.3.6	Procurement	26&lt;br /&gt;
* 2.3.6.1	2.2.6.1 Preparation of Tender Documents	26&lt;br /&gt;
* 2.3.6.2	Tendering process	27&lt;br /&gt;
* 2.3.7	Implementation/Construction Stage	27&lt;br /&gt;
* 2.3.7.1	Contract Management	27&lt;br /&gt;
* 2.3.7.2	Contract supervision and administration	27&lt;br /&gt;
* 2.3.8	Operation and Maintenance Stage	28&lt;br /&gt;
* 2.3.9	Performance Monitoring	28&lt;br /&gt;
* 2.4	Consulting the Integrated Water Resources Management and Development (IWRMD) Plans	28&lt;br /&gt;
* 2.4.1	Status of Development and Implementation of IWRMD Plans	29&lt;br /&gt;
* 2.4.2	Components of IWRMD Plans	30&lt;br /&gt;
* 2.5	Consult Guidelines for Preparation of Water Safety Plans - Resilient to Climate Change	30&lt;br /&gt;
* 2.6	Environmental and Social Impact Assessment Compliance	30&lt;br /&gt;
* 2.6.1	Procedures for Conducting ESIA in Tanzania	31&lt;br /&gt;
* 2.6.2	Strategic Environmental and Social Assessment (SESA) Compliance	31&lt;br /&gt;
* 2.7	Potential Impacts of Climate Change on Water Supply Projects	32&lt;br /&gt;
* 2.8	Participation of Community Based Water Supply Organizations (CBWSO) in Various Planning Stages	32&lt;br /&gt;
* 2.9	References	32&lt;br /&gt;
* CHAPTER THREE	35&lt;br /&gt;
* WATER SOURCES ANALYSIS	35&lt;br /&gt;
* 3.1	Availability of Water Resources in Tanzania Mainland	35&lt;br /&gt;
* 3.2	Water Sources Available in Tanzania Mainland	38&lt;br /&gt;
* 3.2.1	Rainwater and fog harvesting	39&lt;br /&gt;
* 3.2.2	Surface Water	39&lt;br /&gt;
* 3.2.2.1	Rivers or streams	39&lt;br /&gt;
* 3.2.2.2	Impoundments	39&lt;br /&gt;
* 3.2.2.3	Springs	39&lt;br /&gt;
* 3.2.2.4	Lakes	39&lt;br /&gt;
* 3.2.2.5	Dams	40&lt;br /&gt;
* 3.2.3	Groundwater	40&lt;br /&gt;
* 3.2.3.1	Infiltration galleries/wells	40&lt;br /&gt;
* 3.2.3.2	Well	40&lt;br /&gt;
* 3.2.3.3	Classification of wells based on the aquifer tapped	41&lt;br /&gt;
* 3.2.3.3.1	Shallow wells	41&lt;br /&gt;
* 3.2.3.3.2	Deep wells	41&lt;br /&gt;
* 3.2.3.3.3	Artesian wells	41&lt;br /&gt;
* 3.3	Quality Suitability of Water Sources for Water Supply Projects	42&lt;br /&gt;
* 3.4	Pilot Testing of Water Sources for Establishment of Appropriate Treatment	42&lt;br /&gt;
* 3.5	General Considerations for Selection of Water Sources	42&lt;br /&gt;
* 3.5.1	Adequacy and reliability	42&lt;br /&gt;
* 3.5.2	Quality of water sources	43&lt;br /&gt;
* 3.5.3	Technical Requirements	43&lt;br /&gt;
* 3.5.4	Cost implications to develop a water source	43&lt;br /&gt;
* 3.5.5	Protection of water sources	43&lt;br /&gt;
* 3.5.6	Legal and management requirements	44&lt;br /&gt;
* 3.5.7	Distance of water supply source	44&lt;br /&gt;
* 3.5.8	Topography of the project area and its surroundings	44&lt;br /&gt;
* 3.5.9	Elevation of a source of water supply	44&lt;br /&gt;
* 3.6	Determination of water source yield	44&lt;br /&gt;
* 3.6.1	Rainwater and fog harvesting	45&lt;br /&gt;
* 3.6.1.1	Rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.1	Types of rainwater harvesting	45&lt;br /&gt;
* 3.6.1.1.2	Components of rainwater harvesting system	46&lt;br /&gt;
* 3.6.1.1.3	Estimation of the yield	47&lt;br /&gt;
* 3.6.2	Hydrological Analysis of Surface Waters	47&lt;br /&gt;
* 3.7	Other considerations for various water sources	55&lt;br /&gt;
* 3.7.1	Water permits Considerations	55&lt;br /&gt;
* 3.7.2	Conservation of water sources	55&lt;br /&gt;
* 3.8	References	55&lt;br /&gt;
* CHAPTER FOUR	56&lt;br /&gt;
* WATER DEMAND ASSESSMENT	56&lt;br /&gt;
* 4.1	Water Demand Assessment	56&lt;br /&gt;
* 4.2	General Factors Affecting Water Demand Assessment	57&lt;br /&gt;
* 4.3	Determination of Water Demand for Different Uses	58&lt;br /&gt;
* Step 7. Establish Net Water Demand	67&lt;br /&gt;
* Step 9: Establish Operational water consumption	67&lt;br /&gt;
* Step 10: Establish System water losses	68&lt;br /&gt;
* Step 11 Establish Non-Revenue Water	69&lt;br /&gt;
* 4.4	Variations in Water Consumption	70&lt;br /&gt;
* 4.4.1	Definitions	70&lt;br /&gt;
* 4.4.2	Variation in the Rate of Consumption	71&lt;br /&gt;
* 4.4.2.1	Diurnal variation in demand	71&lt;br /&gt;
* 4.4.3	Peak Factors	72&lt;br /&gt;
* 4.4.4	Predicting Demand	74&lt;br /&gt;
* 4.4.5	Design Demand	75&lt;br /&gt;
* 4.5	References	75&lt;br /&gt;
* CHAPTER FIVE	76&lt;br /&gt;
* PIPELINES DESIGN	76&lt;br /&gt;
* 5.1	Design Requirements of pipelines	76&lt;br /&gt;
* 5.2	Types of pipelines	76&lt;br /&gt;
* 5.3	Security considerations for pipelines	76&lt;br /&gt;
* 5.3.1	Methods of water transmission and distribution	76&lt;br /&gt;
* 5.3.2	Gravity flow	77&lt;br /&gt;
* 5.3.3	Pumping with storage	77&lt;br /&gt;
* 5.3.4	Direct pumping to the distribution system	77&lt;br /&gt;
* 5.4	Pipeline Hydraulics Assessment	77&lt;br /&gt;
* 5.4.1	Pressure	77&lt;br /&gt;
* 5.4.2	Determination of Head Losses	77&lt;br /&gt;
* 5.5	Water supply transmission system	79&lt;br /&gt;
* 5.5.1	Determination of Transmission Pipe Size	79&lt;br /&gt;
* 5.5.2	Maximum Pressure	79&lt;br /&gt;
* 5.6	Distribution system	80&lt;br /&gt;
* 5.6.1	Branched System	80&lt;br /&gt;
* 5.6.2	Looped System	81&lt;br /&gt;
* 5.7	Pipe network analysis	82&lt;br /&gt;
* 5.7.1	Network analysis by Conventional method (Hardy Cross)	82&lt;br /&gt;
* 5.7.2	Network Analysis by Computer Software	82&lt;br /&gt;
* 5.7.2.1	EPANET Software	82&lt;br /&gt;
* 5.7.3	Pipeline design criteria	85&lt;br /&gt;
* 5.8	Pipeline materials selection	86&lt;br /&gt;
* 5.8.1	Considerations in Selecting Pipeline Materials	86&lt;br /&gt;
* 5.8.1.1	Flow Characteristics	86&lt;br /&gt;
* 5.8.1.2	Pipe Strength	86&lt;br /&gt;
* 5.8.1.3	Durability	87&lt;br /&gt;
* 5.8.1.4	Type of Soil	87&lt;br /&gt;
* 5.8.1.5	Availability	87&lt;br /&gt;
* 5.8.1.6	Cost of Pipes	87&lt;br /&gt;
* 5.8.2	Types of Pipe Materials Available	87&lt;br /&gt;
* 5.8.2.1	Galvanized Iron (GI) Pipes	87&lt;br /&gt;
* 5.8.2.2	Plastic Pipes	87&lt;br /&gt;
* 5.9	Appurtenances for transmission and distribution mains	88&lt;br /&gt;
* 5.9.1	Valves	89&lt;br /&gt;
* 5.9.1.1	Isolation Valves	89&lt;br /&gt;
* 5.9.1.2	Check Valves	89&lt;br /&gt;
* 5.9.1.3	Float Valves	89&lt;br /&gt;
* 5.9.1.4	Air Release Valves	89&lt;br /&gt;
* 5.9.1.5	Pressure Reducing Valves	89&lt;br /&gt;
* 5.9.1.6	Washout valves	89&lt;br /&gt;
* 5.9.2	Fittings	89&lt;br /&gt;
* 5.10	References	90&lt;br /&gt;
* CHAPTER SIX	91&lt;br /&gt;
* PUMPING SYSTEMS	91&lt;br /&gt;
* 6.1	Introduction	91&lt;br /&gt;
* 6.2	Rationale	91&lt;br /&gt;
* 6.3	Common Types of Pumps used in water supply	91&lt;br /&gt;
* 6.4	Pumping System Setup	91&lt;br /&gt;
* 6.5	Source of Pumping Power	92&lt;br /&gt;
* 6.6	Pumping system design pump selection	92&lt;br /&gt;
* 6.7	Pump Protection	95&lt;br /&gt;
* 6.8	References	95&lt;br /&gt;
* CHAPTER SEVEN	96&lt;br /&gt;
* WATER TREATMENT	96&lt;br /&gt;
* 7.1	Introduction	96&lt;br /&gt;
* 7.1.1	Classification of the qualities of water sources found in Tanzania according to the complexity of its treatment	96&lt;br /&gt;
* 7.1.2	Classification of Unit Operations to achieve water treatment levels	99&lt;br /&gt;
* 7.2	Recommended overall design approach for treatment plant components	99&lt;br /&gt;
* 7.3	Documents and websites consulted and those which are hyper-linked to the DCOM Manual	100&lt;br /&gt;
* 7.4	Water treatment design considerations	100&lt;br /&gt;
* 7.5	Water treatment levels and units	101&lt;br /&gt;
* 7.5.1	Pre-treatment	101&lt;br /&gt;
* 7.5.1.1	Scum and Floating Materials Skimmer	101&lt;br /&gt;
* 7.5.1.2	Screening or straining	101&lt;br /&gt;
* 7.5.1.3	Grit Removal	103&lt;br /&gt;
* 7.5.1.3.1	Design criteria	103&lt;br /&gt;
* 7.5.1.4	Sand Traps	105&lt;br /&gt;
* 7.5.1.5	Pre-chlorination	107&lt;br /&gt;
* 7.5.1.6	Water pre-conditioning (pH adjustment)	108&lt;br /&gt;
* 7.5.2	Primary Treatment	108&lt;br /&gt;
* 7.5.2.1	Sedimentation	108&lt;br /&gt;
* 7.5.2.2	Primary Filtration	114&lt;br /&gt;
* 7.5.2.2.1	Slow Sand Filtration	114&lt;br /&gt;
* 7.5.2.2.2	Rapid Gravity Sand Filtration	117&lt;br /&gt;
* 7.5.2.2.3	Comparison between Slow Sand Filters and Rapid Sand Filters	118&lt;br /&gt;
* 7.5.2.2.4	Other Types of Filters	119&lt;br /&gt;
* 7.5.2.3	Floatation	124&lt;br /&gt;
* 7.5.2.3.1	Dissolved-Air Floatation	124&lt;br /&gt;
* 7.5.2.3.2	Electrolytic Floatation	125&lt;br /&gt;
* 7.5.2.3.3	Dispersed-Air Floatation	125&lt;br /&gt;
* 7.5.2.4	Aeration	125&lt;br /&gt;
* 7.5.2.4.1	Falling Water Aerators	126&lt;br /&gt;
* 7.5.2.4.2	Spray Aerators	127&lt;br /&gt;
* 7.5.3	Secondary Treatment	130&lt;br /&gt;
* 7.5.3.1	Clarification	130&lt;br /&gt;
* 7.5.3.2	Coagulation	130&lt;br /&gt;
* 7.5.3.3	Flocculation	131&lt;br /&gt;
* 7.5.3.4	Filtration	131&lt;br /&gt;
* 7.5.4	Tertiary Treatment	132&lt;br /&gt;
* 7.5.4.1	Disinfection	132&lt;br /&gt;
* 7.5.4.1.1	Disinfection Methods	132&lt;br /&gt;
* 7.5.4.1.2	Chlorinators	132&lt;br /&gt;
* 7.5.4.1.3	Design considerations for chlorinators	133&lt;br /&gt;
* 7.5.4.2	Ozonation	133&lt;br /&gt;
* 7.5.4.3	Water softening	134&lt;br /&gt;
* 7.5.4.3.1	Methods of Softening	135&lt;br /&gt;
* 7.5.4.4	Defluoridation of Water	139&lt;br /&gt;
* 7.5.4.4.1	Fluorides	139&lt;br /&gt;
* 7.5.4.4.2	Defluoridation	139&lt;br /&gt;
* 7.5.4.5	Water Conditioning	141&lt;br /&gt;
* 7.5.5	Management of Water Treatment Sludge	141&lt;br /&gt;
* 7.5.5.1	Treatment of Water Treatment Sludge	141&lt;br /&gt;
* 7.5.5.1.1	Sludge Thickening	141&lt;br /&gt;
* 7.5.5.1.2	Sludge Dewatering	143&lt;br /&gt;
* 7.5.5.1.3	Sludge Drying Beds	144&lt;br /&gt;
* 7.5.5.1.4	Sludge Lagoons	144&lt;br /&gt;
* 7.5.5.1.5	Mechanical Sludge Dewatering	145&lt;br /&gt;
* 7.5.5.1.6	Backwash Water Recovery	145&lt;br /&gt;
* 7.5.5.1.7	Waste from Slow Sand Filters	146&lt;br /&gt;
* 7.5.5.2	Disposal of sludge	147&lt;br /&gt;
* 7.6	References	147&lt;br /&gt;
* CHAPTER EIGHT	148&lt;br /&gt;
* TREATMENT OF WATERS WITH SPECIAL CONTAMINANTS	148&lt;br /&gt;
* 8.1	Natural Organic Matter	148&lt;br /&gt;
* 8.2	Arsenic	149&lt;br /&gt;
* 8.3	Radioactive	149&lt;br /&gt;
* 8.4	Fluoride removal from drinking water	149&lt;br /&gt;
* 8.5	Toxic Cyanobacteria in Drinking Water	150&lt;br /&gt;
* 8.6	Available methods for removal of special water contaminants	152&lt;br /&gt;
* 8.7	Desalination	152&lt;br /&gt;
* 8.7.1	Additive method	152&lt;br /&gt;
* 8.7.2	Adsorption methods	153&lt;br /&gt;
* 8.7.3	Capacitive deionization (CDI)	153&lt;br /&gt;
* 8.7.4	Membrane Filtration	154&lt;br /&gt;
* 8.7.5	Reverse Osmosis	156&lt;br /&gt;
* 8.8	References	158&lt;br /&gt;
* CHAPTER NINE	159&lt;br /&gt;
* DESIGN OF WATER STRUCTURES	159&lt;br /&gt;
* 9.1	Sizing and Locating Water Structures	159&lt;br /&gt;
* 9.1.1	Tanks	159&lt;br /&gt;
* 9.1.1.1	Storage tanks	159&lt;br /&gt;
* 9.1.1.2	Sedimentation/Settling Tanks	160&lt;br /&gt;
* 9.1.1.3	Break Pressure Tanks	161&lt;br /&gt;
* 9.1.2	Water Intakes	162&lt;br /&gt;
* 9.1.3	Dams	164&lt;br /&gt;
* 9.1.3.1	Engineering Classification of Dams	164&lt;br /&gt;
* 9.1.3.2	Size classification of dams	164&lt;br /&gt;
* 9.1.3.3	Feasibility and geotechnical investigations	166&lt;br /&gt;
* 9.1.3.4	Hydrological analysis of the catchment	167&lt;br /&gt;
* 9.1.4	Geotechnical Investigation	169&lt;br /&gt;
* 9.1.4.1	Design of dams	170&lt;br /&gt;
* 9.1.5	Boreholes	173&lt;br /&gt;
* 9.1.5.1	Groundwater prospecting	179&lt;br /&gt;
* 9.1.5.2	Drilling	182&lt;br /&gt;
* 9.1.5.3	Siting of Well/Borehole	182&lt;br /&gt;
* 9.1.5.4	Well design	183&lt;br /&gt;
* 9.1.5.5	Pumping Tests	183&lt;br /&gt;
* 9.1.5.6	Groundwater quality	187&lt;br /&gt;
* 9.1.6	Water points and Service connections	190&lt;br /&gt;
* 9.1.7	Common Types of Water Points	191&lt;br /&gt;
* 9.1.8	Minimum Technical Requirements of Water Points	191&lt;br /&gt;
* 9.1.9	Criteria  for Design of Water Point/Kiosks	191&lt;br /&gt;
* 9.1.10	Location Considerations for Water Points	192&lt;br /&gt;
* 9.1.11	Technical Tips to Improve Water Points	193&lt;br /&gt;
* 9.1.11.1	Rainwater harvesting	196&lt;br /&gt;
* 9.1.11.2	Fog harvesting	200&lt;br /&gt;
* 9.2	Structural Design of Concrete	201&lt;br /&gt;
* 9.2.1	Structural requirements	201&lt;br /&gt;
* 9.2.2	Methods	201&lt;br /&gt;
* 9.2.2.1	Working Stress Method	201&lt;br /&gt;
* 9.2.2.2	Ultimate Load Method	201&lt;br /&gt;
* 9.2.2.3	Limit State Method	201&lt;br /&gt;
* 9.3	References	201&lt;br /&gt;
* CHAPTER TEN	203&lt;br /&gt;
* APPLICATION SOFTWARE	203&lt;br /&gt;
* 10.1	Application Software Contexts	203&lt;br /&gt;
* 10.2	Recommended Application Software	203&lt;br /&gt;
* 10.2.1	Distribution Network Design Software	203&lt;br /&gt;
* 10.2.1.1	Epanet	203&lt;br /&gt;
* 10.2.1.2	AutoCAD	204&lt;br /&gt;
* 10.2.1.3	WaterCAD	204&lt;br /&gt;
* 10.2.1.4	WaterGEMS	204&lt;br /&gt;
* 10.2.1.5	KY PIPES	204&lt;br /&gt;
* 10.2.1.6	GeoNode	204&lt;br /&gt;
* 10.2.1.7	AutoStudio	204&lt;br /&gt;
* 10.2.1.8	InfoWater	205&lt;br /&gt;
* 10.2.1.9	GIS Software	205&lt;br /&gt;
* 10.2.1.10	MS Project	205&lt;br /&gt;
* 10.2.2	Operation and Maintenance Software	205&lt;br /&gt;
* 10.2.2.1	MS Project	205&lt;br /&gt;
* 10.2.2.2	Excel	205&lt;br /&gt;
* 10.2.2.3	EDAMS	206&lt;br /&gt;
* 10.2.3	Water Quality	206&lt;br /&gt;
* 10.2.3.1	WaterCAD	206&lt;br /&gt;
* 10.3	Supervisory, Control and Data Acquisition (SCADA) Systems	206&lt;br /&gt;
* 10.4	References	207&lt;br /&gt;
* CHAPTER ELEVEN	208&lt;br /&gt;
* METERING	208&lt;br /&gt;
* 11.1	Introduction	208&lt;br /&gt;
* 11.2	Types of Water Meters	208&lt;br /&gt;
* 11.3	Prepaid Meters	208&lt;br /&gt;
* 11.4	Types of Prepaid water models commonly used in Tanzania	209&lt;br /&gt;
* 11.5	Importance of Prepaid Water Metering	210&lt;br /&gt;
* 11.6	Design Considerations for Prepaid Water Meters	210&lt;br /&gt;
* 11.7	Design considerations for prepaid public standpipes	211&lt;br /&gt;
* 11.8	Design consideration for individual domestic customer	212&lt;br /&gt;
* 11.9	Design consideration for Commercial and Institutional Customers	212&lt;br /&gt;
* 11.10	Importance of integrating Prepaid with Post paid revenue management	212&lt;br /&gt;
* 11.11	Selection Criteria for Prepaid water meters	212&lt;br /&gt;
* 11.12	References	214&lt;br /&gt;
* 11.13	Internet Links:	216&lt;br /&gt;
* CHAPTER TWELVE	217&lt;br /&gt;
* DESIGN STANDARDS AND SPECIFICATIONS	217&lt;br /&gt;
* 12.1	Design Standards	217&lt;br /&gt;
* 12.2	Specifications	218&lt;br /&gt;
* 12.3	Materials	218&lt;br /&gt;
* 12.3.1	Building Materials	218&lt;br /&gt;
* 12.3.2	Materials Testing	219&lt;br /&gt;
* 12.3.2.1	Aggregates	219&lt;br /&gt;
* 12.3.2.2	Water	221&lt;br /&gt;
* 12.3.2.3	Cement	221&lt;br /&gt;
* 12.3.2.4	Concrete Works	221&lt;br /&gt;
* 12.3.2.5	Steel	222&lt;br /&gt;
* 12.4	Soil Test	222&lt;br /&gt;
* 12.4.1	Methodology of conducting Soil Investigation for borehole and test pit	222&lt;br /&gt;
* 12.4.2	Soil Investigation for dams	223&lt;br /&gt;
* 12.4.3	Suitability of soil materials for dam construction	223&lt;br /&gt;
* 12.4.4	Determination of In-Situ Bearing Capacity of the Soil	224&lt;br /&gt;
* 12.5	References:	227&lt;br /&gt;
* CHAPTER THIRTEEN	228&lt;br /&gt;
* ROLE OF STAKEHOLDERS IN DESIGN OF WATER SUPPLY PROJECTS	228&lt;br /&gt;
* 13.1	Types of Stakeholders	228&lt;br /&gt;
* 13.2	Roles of stakeholders	228&lt;br /&gt;
* 13.3	References	230&lt;br /&gt;
* APPENDIX A: CLIMATE CHANGE AND RESILIENCE TO CLIMATE CHANGE	232&lt;br /&gt;
* APPENDIX B: MINIMUM WATER FLOW REQUIREMENT FOR FIRE FIGHTING	237&lt;br /&gt;
* APPENDIX C: EXAMPLE: ESTIMATING THE CAPACITY OF TANK	239&lt;br /&gt;
* APPENDIX D: STRUCTURAL DESIGN OF CONCRETE	241&lt;br /&gt;
* APPENDIX E: SUPPLY PUMPING SYSTEMS	251&lt;br /&gt;
* APPENDIX F: SOURCE OF PUMPING POWER	263&lt;br /&gt;
* APPENDIX G: ADDITIONAL DETAILS OF VARIOUS UNIT OPRATIONS	275&lt;br /&gt;
* APPENDIX H: METHODS FOR DISINFECTING WATER	281&lt;br /&gt;
* APPENDIX I: MEASUREMENTS OF WATER HARDNESS	287&lt;br /&gt;
* APPENDIX J: BASIC STATISTICS USED IN ESTIMATION OF DESIGN OF FLOOD EVENTS	289&lt;br /&gt;
* APPENDIX K: DAMS DETAIL DESIGN	294&lt;br /&gt;
* APPENDIX L: STANDARD DRAWINGS	306&lt;br /&gt;
* APPENDIX M: SELECTED INTAKE DESIGNS.	307&lt;br /&gt;
* SUBJECT INDEX	309&lt;br /&gt;
*&lt;/div&gt;</summary>
		<author><name>Jlungo</name></author>
		
	</entry>
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