Water Quality and Health Impacts in Rural Water Schemes Matthew W. - - PowerPoint PPT Presentation

water quality and health impacts in rural water schemes
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Water Quality and Health Impacts in Rural Water Schemes Matthew W. - - PowerPoint PPT Presentation

Water Quality and Health Impacts in Rural Water Schemes Matthew W. Hurst , Mamaru A. Moges School of Civil and Environmental Engineering, Cornell University School of Civil and Water Resources Engineering, Bahir Dar University


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Water Quality and Health Impacts in Rural Water Schemes

Matthew W. Hurst¹ , Mamaru A. Moges² ¹ School of Civil and Environmental Engineering, Cornell University ² School of Civil and Water Resources Engineering, Bahir Dar University

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Introduction

  • CMP is a system that is well established as a

sustainable way to implement and maintain rural community water points

  • However, the direct health impacts have not been

studied extensively.

  • Research questions include:

– Does construction of the scheme and providing scheme water changes the health status of the computer? – If so, how does this change community health status? – Is there a link between functionality, sustainability, and health?

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Functionality, sustainability, and health

  • Health: self-reported incidence in the past

year of diarrheal disease and other waterborne diseases

  • Sustainability: long term functionality
  • Functionality: accessibility and coverage

– Accessibility: number of hours in a day water is available for the community – Coverage: % of community population that lives within 1.5 km of the water source

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Study Area-Sostu Tirba

  • Study area was the most

seriously affected in 2008 by AWD outbreak (Acute Water Diarrheal)

  • The Woreda Health Office

and Water Resource Development Office reports 100% sanitation coverage and 100% water coverage

  • We want to investigate if

these claims are true given the outbreak of AWD

  • There are enough CMP and

non-CMP water points in the kebele of Sostu Tirba for comparison

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Objectives

  • Development of methodology for indexing

sustainability of rural water supply schemes

  • Study how hygiene and WASH infrastructure

are related to household health (measured as self-reported waterborne disease incidence)

  • WASH mapping for these communities
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Materials and Methods

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Surveys and Interviews

  • Survey has 150 questions divided into 8 sections

(based on WHO/UNICEF, 2004)

– (1) general information – (2) socio-economic conditions – (3) water supply – (4) transport, handling and storage of water – (5) hand washing behavior – (6) latrine use – (7) other sanitation and hygiene behaviors – (8) health

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2 2 2

) 1 ( ) 1 ( ) 1 ( z p p N e N p p z n     

Gott/Scheme Number of households Sample size

Amicha 35 26 Betena 52 34 Chimna 43 30 Degegno 45 31 Gimar 50 34 Jagita 42 30 Jalta 16 14 Jomera 58 37 Jomeram 3 3 KesMen 45 31 KidaneM 54 35 Kiflusta 39 28 KiIaj2 49 33 KilajI 48 33 Lacosta 36 27 Manaja 44 31 Mesekela 54 35 Shumasta 52 34 Sigure M 48 33 TachJ1 46 32 TachJ2 44 31 Walkiti 63 39 Yemala1 49 33 Yemala2 32 25

Total Number Surveys 719

Where: N is the total number of households in Tirba, p is the expected proportion

  • f people who are expected

to have waterborne disease (since this unknown, a 50% value was chosen as this yields maximum sample size), e is the confidence interval (±10%) and z is a standard variate from a normal distribution (at the 95% confidence level , z = 1.96).

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Interview with WASHCos and Pump Attendants

WASHCos:

  • Quality and presence of

documentation

  • Financial management by

WASHCo including fee collection structure

  • Management of the

scheme (i.e., availability

  • f spare parts, etc.)
  • Water quality and water

safe planning: procedures and records

Pump Attendant:

  • Training
  • Roles and responsibilities

regarding operation and maintanence

  • Functionality of the

system

  • Areas for improvement
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Water Quality

  • Assess microbiological and physical-chemical

quality through turbidity and bacteriological tests

  • Water is taken from the source and household

level

  • For the household water quality was assessed

for transport, transfer, and drinking vessels

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SLIDE 11
  • 3. Materials and Method: Methods
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Sustainability Index

Total of 20 indicator variables used in developing the index PCA (Principal Component Analysis) of three components

– Functionality – governance and operation and maintenance – and community opinion

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Component Factors Scoring Factor Component 1-Governance and Operation and Maintenance

Public Hearings Held 0.87 Public Audit Held 0.91 Bank Account Present 0.94 Tariff Collection System 0.87 Attendant at Scheme 0.73 Committee 0.86 Implementation Fee Collected 0.71 Spare Parts Available 0.89

Component 2-Community Opinion of Water Scheme and WASHCo

Household Feels Consulted in the Decision-making Processes 0.84 Household Feels Price is Fair 0.91 Household Feels System is Well-managed Financially 0.87 Household is Confident that System Attendants can Fix Problems as they Arise 0.61 Household is Confident that the Overall Training the WASHCo and System Attendants Received is Adequate 0.59 Household feels that they can Afford all the Water that they want 0.28 Household Members Attended Planning and Public Meetings 0.15

Component 3-Functionality of Scheme

Average Hours per Day Water is Supplied 0.91 Household Ranking of Water Quality during the Dry Season 0.91 Household Ranking of Water Quality during the Wet Season 0.96 Training for Operation and Maintenance was Available when System was Implemented 0.43 Amount of Birr (re-scaled) Collected Each Year 0.47

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Results and Discussion

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CMP and Non-CMP Sustainability Index

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Why are CMP schemes more sustainable?

Some, but not all CMP system have better administration in documenting the collection process for tariffs and in carrying out fee collection.

  • This high level of governance and operation and maintenance rating

is reflected in the requirements of communities that apply for schemes: they must have a functioning WASHCo that is trained specifically in implementation and daily operating procedures.

  • Higher community participation is the result of the community

having greater confidence in the ability of the system attendant to

  • perate and maintain CMP schemes and in the WASHCo to manage

the scheme.

  • High community opinion is also related to the community’s

willingness to pay for the water service and the likelihood that WASHCo will collect future fees. The functionality was also higher and may be in large part due to the higher numbers of system attendants at CMP points compared to non-CMP points.

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Sustainability and Diarrheal Disease

Sustainability Diarrheal Disease

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Sustainability index overlayed with diarrheal disease incidence

Significant factors impacting diarrheal disease

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Variables having major impact

Factor Coefficient (β) Standard Error P-value Adjusted Odds Ratio Open Defecation 0.94 1.10 0.39 2.56 Open Defecation Practiced Before Health Campaign 1.45 0.86 0.09 4.25 Hand Washing Station Located by Latrine 0.68 0.69 0.33 1.97 ‘Proper’ Defecation Practice on Farm 1.05 0.77 0.17 2.85 Animals Have Separate Dwelling from Human Beings 1.28 0.74 0.08 3.59 Irrigation Practiced

  • 1.30

0.54 0.02 0.27 Proper Disposal of Solid Waste

  • 0.31

0.57 0.59 0.74 Constant

  • 0.77

3.23 1.00 0.46

Analysis of variance for model: adjusted R2 = 0.18, degrees of freedoms in regression = 7,

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Currently, does water quality at the source matter?

18 households overall, n = 61 samples Source water quality did not show up as a significant variable in the multivariate Regression model as impacting human health  WHY? Very little association between diarrheal illness incidence and sustainability or functionality of water source. However, there are two concerns with justifying that improved water source necessarily equates with significantly improved health: (1) source water cannot be safe unless well protected and ultimately disinfected by some means, and (2) disease incidence is related to a plethora of other WASH variables such as utilization of a latrine, hand washing, etc.

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Transfer vessel contamination

  • There is also an average increase of 35% between transfer

vessels and drinking vessel.

  • Such results suggest that the drinking vessel provides a

surface for water contamination resulting from poor household handling practices. The most likely practice that causes contamination is that the household often wipes the glass out by hands.

  • Another household practice is leaving standing water in the

glass.

  • The quality of water for washing dishes is often recycled and

below the quality of the source water, however, there is not a significant amount of water left in the glass to probably significantly increase contamination,

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Conclusions

  • CMP are far more sustainable compared to non-CMP systems.

Due to: (1) governance and operation and maintenance and (2) community opinion.

  • Sustainability of water points is not correlated with final source water

contamination at the household level Even though these schemes give much greater and higher quality of water access to women, there is no evidence that the final contamination in the household is affected by initial source water quality. In addition to this finding, even protected sources have high contamination at the household level.

  • These two findings together suggest that leaving a residual of chlorine in

source water would provide a protective barrier to some of the poor hygienic storage and handling practices of water in the households

  • Even protected sources can still have high contamination at the household

level resulting from poor hygienic handling and storage practices at the household level.