Published on in Vol 10 (2024)

This is a member publication of University of Oxford (Jisc)

Preprints (earlier versions) of this paper are available at https://preprints.jmir.org/preprint/42462, first published .
The Impact of Rapid Handpump Repairs on Diarrhea Morbidity in Children: Cross-Sectional Study in Kwale County, Kenya

The Impact of Rapid Handpump Repairs on Diarrhea Morbidity in Children: Cross-Sectional Study in Kwale County, Kenya

The Impact of Rapid Handpump Repairs on Diarrhea Morbidity in Children: Cross-Sectional Study in Kwale County, Kenya

Original Paper

1School of Geography and the Environment, University of Oxford, Oxford, United Kingdom

2Department of Engineering Science, University of Oxford, Oxford, United Kingdom

3Department of Geography and Sustainable Development, University of Miami, Coral Gables, FL, United States

4Department of Public Health Sciences, University of Miami, Miami, FL, United States

5Barts Health NHS Trust, London, United Kingdom

6London School of Hygiene & Tropical Medicine, London, United Kingdom

Corresponding Author:

Patrick Thomson, MEng, PhD

Department of Engineering Science

University of Oxford

Old Road Campus Building

Headington

Oxford, OX3 7DQ

United Kingdom

Phone: 44 1865 617675

Email: patrick.thomson@ouce.ox.ac.uk


Background: Handpumps are used by millions of people as their main source of water. Although handpumps represent only a basic form of water provision, there have been continuous efforts to improve the performance of these systems as they are likely to remain in use for many years to come. The introduction of a professional maintenance service in southern Kenya has shown an order of magnitude improvement in operational performance over community-based management, with 90% of handpump faults repaired within 3 days of being reported. One driver behind these efforts is the assumption that a more reliable water supply will lead to a reduction in water-related disease. However, it is not clear if operational improvements lead to health gains. Despite limited empirical evidence, some modeling studies suggest that even short periods of drinking contaminated water can lead to disproportionate negative health impacts.

Objective: The aim of this study was to assess whether the improvements in operational performance from the rapid professional maintenance of rural handpumps lead to improved household health outcomes.

Methods: From a sample of households using handpumps as their primary water source in Kwale County, Kenya, we measured the 2-week prevalence of World Health Organization–defined diarrhea in children, reported by the adult respondent for each household. We compared the rates before and after a period during which the households’ handpumps were being professionally maintained. We then conducted a cross-sectional analysis, fitting logistic regression models with reported diarrhea as the dependent variable and speed of repair as the independent exposure of interest, adjusting for household socioeconomic characteristics; dwelling construction; and Water, Sanitation, and Hygiene (WASH)-related factors. We fitted an additional model to examine select interactions between covariates.

Results: Reported diarrhea in children was lower in households whose pumps had been repaired within 24 hours (adjusted odds ratio 0.35, 95% CI 0.24-0.51). This effect was robust to the inclusion of multiple categories of covariates. No reduction was seen in households whose pump repairs took more than 24 hours. Analysis of interaction terms showed that certain interventions associated with improved WASH outcomes were only associated with reductions in diarrhea in conjunction with socioeconomic improvements.

Conclusions: Only pump repairs consistently made within 24 hours of failure led to a reduction in diarrhea in the children of families using handpumps. While the efficacy of reduction in diarrhea is substantial, the operational challenges of guaranteeing same-day repairs limits the effectiveness of even best-in-class pump maintenance. Maintenance regimes that cannot bring handpump downtimes close to zero will struggle to generate health benefits. Other factors that reduce diarrhea prevalence have limited effect in isolation, suggesting that WASH interventions will be more effective when undertaken as part of more holistic poverty-reduction efforts.

JMIR Public Health Surveill 2024;10:e42462

doi:10.2196/42462

Keywords



In rural areas with no grid electricity or limited funds to run diesel generators, many communities depend upon handpumps to access shallow groundwater for their daily water needs. Groundwater, in contrast to surface water, is more likely to be available year-round and less likely to require treatment to be potable [1]. Despite efforts throughout the period of the Millennium Development Goals and now in response to Sustainable Development Goal (SDG) 6.1, “safely managed water for all,” millions of people will still be relying on water from handpumps beyond 2030. While “safely managed” water—as defined by the World Health Organization (WHO)/United Nations Children’s Fund (UNICEF) Joint Monitoring Programme (JMP) as the use of “an improved drinking water source which is located on premises, available when needed, and free of fecal and priority chemical contamination”—remains the goal for water services for all, the size of the task and difficulty in achieving this goal has been acknowledged through the JMP Service Ladder’s inclusion of an interim service level of “basic” water, the category that includes most handpumps [2].

There are many reasons for aspiring to the goal of safely managed water for all. One of the main drivers of this goal—and Water, Sanitation, and Hygiene (WASH) interventions more generally—has been the understanding that disease morbidity can be reduced through better water service provision [3]. Piped water to the home, the most usual conception of safely managed water, is associated with lower morbidity, in particular of diarrheal disease [4]. However, with 26% of the world’s population—and 73% in sub-Saharan Africa—still lacking safely managed water and the achievement of SDG 6.1 unlikely at current rates of progress [5], it is important to understand the health implications of having only a basic water supply, as these are at risk of contamination [6], which can lead to diarrheal disease [7].

The contribution of diarrheal disease to the worldwide disease burden is falling but remains substantial [8]. Diarrhea itself contributes to the burden of disease for individuals and consequently to the global burden of disease estimates. Diarrhea is the cause of 1.31 million deaths worldwide, with 303,045 of those being of children under 5 years of age in sub-Saharan Africa; for that same demographic, diarrhea also causes 27 million disability-adjusted life years (DALYs) [9], which corresponds to approximately one in every seven DALYs. Diarrhea interacts with nutrition, reducing nutrient absorption [10,11]; therefore, this figure may significantly underestimate the disease burden from diarrhea by up to 39% [12]. Again, this is especially egregious in children, as undernutrition can produce long-term, nonrecoverable negative impacts on physical and cognitive development [13-16], with associated long-term economic and welfare impacts and related policy implications [17,18].

Community-based management, the model by which local communities are responsible for the repair and maintenance of their pumps, became the default management model for rural water supply in the late 1970s, with mixed success [19-24], and an estimated one in four handpumps in sub-Saharan Africa are out of action today [25]. Since the 2000s, there has been increasing interest in professional management models more akin to how urban piped water systems are run, whether directly by governments or subcontracted to a water service provider [26-29]. More recent evidence indicates that communities do have a preference for private sector involvement in service provision over community management or direct government provision, but only if service performance is high [30-32].

We here present results obtained from a cross-sectional survey following the introduction of a professional handpump maintenance service in Kwale County in southern Kenya. The service was initially funded by a research program that was investigating whether the intervention of a rapid, professional repair service, supported by data measuring handpump use using sensors attached to the pumps [33], could result in repairing handpumps faster than had been the case under community-based management. The rapid repair service reduced average pump downtimes from approximately 1 month to a few days, an improvement that is valued by households and communities [34-37]. This study examined whether this improvement in service performance also led to health benefits. Although there is limited empirical evidence to inform service decisions, some studies suggest that even the shortest periods of drinking contaminated drinking water can lead to disproportionate negative health impacts [38,39], implying a threshold effect with a nonlinear relationship between quality of service and the health benefits of that service. Obtaining empirical evidence about this relationship would inform both local operational decisions and wider WASH policy, and in doing so shed light on the role of handpumps in meeting SDG 6.1.

We hypothesized that shorter pump downtimes resulting from the professional maintenance service would be associated with lower rates of child diarrhea. We examined this by combining data on pump failures and subsequent repairs, generated by the pump mechanics, with self-reported child diarrhea data from households that were surveyed before the repair service was introduced and after 18 months of the service. To overcome the challenges associated with an observational study, we analyzed the data using two complementary techniques. The first technique compared child diarrhea prevalence (during a 2-week period) in the same households before and after the repair service was introduced to control for time-invariant household characteristics. The second approach involved a cross-sectional analysis comparing households reporting diarrhea with those not reporting diarrhea, adjusting for household characteristics gathered at the same time as the self-reported diarrhea data.


Study Area

This study took place in Kwale County, located on the southern coast of Kenya between Mombasa and the border with Tanzania. This region covers an area of around 8300 km2 and has a population of 720,000 that is 82% rural, with the seventh-highest poverty rate among Kenya’s 47 counties. The study area was limited to the Msambweni and Matuga subcounties closer to the coast, covering an area of around 2200 km2. The coastal climate has a bimodal rainfall pattern with an average annual precipitation of 1400 mm with significant interannual variability.

Within the study area there is heterogeneity both in socioeconomic characteristics and physical geography. We simplified the study area into three geographical zones for the purposes of analysis (see Figure 1) [36]. In the area in and around the urban center of Ukunda, the population density is higher and there are more alternative sources of water available during handpump breakdowns. There is also easier access to medical facilities in this area. Inland, where shallow wells are supplemented by deeper boreholes drawing water from sandstone, the population is less dense and livestock ownership is more common. Being more sparsely populated makes access to other sources of water more challenging; however, the deeper boreholes into the sandstone enable better source protection relative to shallow wells and improve the likelihood of a given handpump producing uncontaminated water. This is in contrast to the coastal strip where the population is still rural but the density is higher. Alternative nonsurface water sources in the form of other handpumps and shallow wells are relatively close by. However, this proximity of other sources, combined with the high population density and the fact that the wells in this area are mostly shallow and were hand-dug into the karstic coral, make source protection extremely difficult in this area.

Figure 1. Map of the study area in Kwale County, Kenya, with the locations of handpumps marked in zones defined in Katuva et al [36]. Red indicates coastal, green indicates inland, and blue indicates Ukunda.

Handpump Repair Service

The professional repair service was set up in Kwale as part of a project examining whether professional handpump maintenance, aided by better data on handpumps, could lead to reduced pump downtimes [33,40]. A waterpoint mapping exercise was undertaken in August 2013, recording the location and functionality of the handpumps in the study area, along with basic information about pump repair and management arrangements. A total of 626 pumps were found, with 351 identified as having been functional during the previous 12 months. We then set up an office in Msambweni, near the center of the study area, and recruited two experienced pump fundis (mechanics) and a manger. Two hundred handpumps were offered a free maintenance service, which corresponded to all of the functioning handpumps in a smaller geographical area across Msambweni and Matuga subcounties. The service started in February 2014 and continued until the end of 2015.

We provided the mechanics with motorbikes, tools, and a stock of spare parts to be able to quickly respond to handpump failures and complete most repairs during a single visit to the pump. When repairs required more labor, such as removing rising mains, the communities provided pro-bono support to the mechanics. Toward the end of 2015, we spun the repair service out from the research program, establishing it as an independent locally owned entity, named FundiFix. At this point, communities were given the opportunity to continue receiving the maintenance service through paying a heavily subsidized monthly fee [41].

Data Sources

The study timeline is schematically summarized in Figure 2. Building on the mapping exercise completed in August 2013, a more extensive household survey was conducted in October and November 2013. A total of 2508 households who had access to a functioning handpump were surveyed, randomly selected from those using each of the 351 functional handpumps identified during the earlier waterpoint mapping exercise. Household selection was made by the enumerator team leader, selecting a direction and distance from the pump for each enumerator based on a throw of a six-sided die. A mean of 7.1 households were interviewed per handpump.

Figure 2. Timeline of activities that generated data used in this study.

The survey questionnaire included questions on household makeup and demographics; socioeconomic status, including key consumption and wealth indicators; basic self-reported health indicators for each household member; water use, collection, and storage; and waterpoint institutional arrangements, payment policies, and behavior. These questions were asked of one respondent for each household. For this study, we used the presence or absence of diarrhea reported for children in the household in the 2 weeks prior to the survey as the primary outcome measure; the other items were considered as covariates in the analysis. The only variable used from the 2013 survey was self-reported diarrhea in the 2 weeks prior to the survey.

A second household survey was conducted in March, April, and May of 2015. This was a repeat of the first survey, the aim being to see what had changed for the communities in the study area during the time of the project, specifically in relation to the pump repair service. The two surveys were matched: 59% were matched by household and respondent, 30% were matched by household but not respondent, and the remaining 11% represent cases where a different family/household was living in the dwelling. All the socioeconomic data used in this study were from the 2015 survey as these data represented the households’ situation during the time they were receiving the free repair service. At the time of this survey, the maintenance service had been operational for at least 12 months.

The two mechanics and their manager who were providing the handpump maintenance service kept detailed records of repairs undertaken, the most significant details being when the breakdown was first identified, when they attended, and when the repair was completed. These records yielded the time and duration of pump outages. Over the whole period, 599 repairs were completed on 169 pumps. The time between a breakdown being reported and repaired varied due to factors such as the complexity of the required repair, the geographical remoteness of the pump, and other logistical or operational constraints. The majority of repairs (90%) were completed within 3 days of a breakdown—the stated target of the service—and 44% were repaired within 24 hours of the fault being reported.

Blinding and Concealment

Efforts were made to ensure blinding and concealment when collecting the data. The enumerators were blinded to the intervention as, other than being aware that the mechanics were operating in the area as part of another University of Oxford–funded research project, they had no knowledge of which pumps had been repaired. While the households were certainly not blinded to whether or not they had had a repair, it would not have been readily apparent to participants that the questions about their household members’ health were to be linked to the repairs, because the health questions were part of a large questionnaire and questions about the pump were intentionally asked in a later section of the survey than the health questions.

Mirroring the enumerators, the mechanics had very little knowledge of the household surveys. They were aware that the first household survey had taken place and that the second was occurring, and that it was broadly connected to their work, but they were not in any way involved in the survey. Treatment allocation—in this case, pump repair by the mechanics—could not be entirely randomized given that chance and other factors, measurable or otherwise, will have led to pump breakdown; however, the mechanics’ responses to reported breakdowns were unpredictable and not influenced by the enumerators or research team.

Inclusion Criteria

A total of 1451 households used pumps that were offered the free repair service. Out of these, 294 were excluded as our mechanics had not made a repair to their handpumps during the trial period. A further 182 were excluded as it was reported during the household survey that the reference handpump was not their primary water source. Finally, 135 were excluded as there were no children reported in the household, leaving a sample of 840 households served by 139 pumps. These pumps received 412 repairs, of which 41% were repaired within 1 day and 39% more within 2 days. The longest repair time was 11 days. In the self-controlled analysis, an additional 89 households were excluded because the families living in the dwelling had changed between the two surveys.

Statistical Analysis

Using the data from the second household survey, we first performed bivariate analysis to test the relationship between speed of pump repairs and self-reported diarrhea. We then used the household-matched data from the first survey to compare the period prevalence of diarrhea reported in 2013 against repair performance measured in 2015. This was to determine whether any relationship between the outcome and exposure was due to time-invariant characteristics of the household that were somehow correlated to the speed of repairs and not due to the repair service itself.

We then performed a cross-sectional analysis, fitting multivariable logistic regression models of self-reported diarrhea using the data from the 2015 household survey to adjust for covariates that have been shown to affect diarrhea period prevalence in the WASH-related literature. We fitted a series of multivariable regression models that iteratively adjust for an additional thematic block of covariates: (1) socioeconomic factors, (2) dwelling factors, and (3) WASH factors (see the Results for detailed factors). Additionally, we fitted a model with interaction terms to further explore results of the first three models, which was also guided by the WASH-related literature. Standard errors were adjusted for clustering using the three geographical zones to control for potentially unobserved/unquantified factors that are hypothesized to be correlated among households within each zone [42]. Because multiple households typically share a handpump, the handpump was another potential analytical unit for the clustering of standard errors between households. As a robustness check, we performed an additional analysis that clustered errors by pump instead of geographical zone.

All statistical analyses were undertaken with Stata version 14.2 (StataCorp, College Station, TX, USA).

Ethical Considerations

This research was conducted with permission from Kenya’s National Council for Science and Technology and with ethics approval from the University of Oxford’s Central University Research Ethics Committee (CUREC reference: SOGE C1 13-125). Informed consent was given by all research participants, all of whom were aged 18 years or over.


Unadjusted Analysis

Bivariate logistic regression models did not provide evidence of any association between households reporting diarrhea and the number of repairs performed on their respective handpumps or the time elapsed since the most recent repair. However, this analysis did reveal an association between the speed of repairs (or pump downtime) and reported diarrhea (Table 1). Pumps consistently repaired within 24 hours upon a breakdown, irrespective of the number of repairs, were associated with a lower reported diarrhea rate. This effect disappeared when analyzed against longer repair times (Table 2).

The analysis comparing the same exposure of rapid repairs in 2015 but with the outcome of self-reported disease from the same household in 2013 (ie, when the repair service could not have had any influence) showed no effect. This suggests that the disease reduction was not due to unobserved time-invariant household characteristics that were somehow correlated with the speed of repairs. Rates of reported diarrhea were comparable between the two surveys: 8.2% in 2013 (dry season) and 9.8% in 2015 (wet season).

Table 1. Bivariate logistic regression analysis of child diarrhea with number and speed of repairs.
Intervention/exposureUnadjusted odds ratio (95% CI)Analysis type
Number of repairs (2015)0.95 (0.85-1.07)Cross-sectional
Days since last repair (2015)1.00 (1.00-1.00)Cross-sectional
Pump repairs within 24 hours

20150.40 (0.27-0.58)Cross-sectional

20131.01 (0.44-2.29)Self-controlled
Table 2. Relative risk of households reporting child diarrhea for different repair speeds.
Intervention/exposureNumber of householdsHouseholds reporting diarrhea, n (%)Rate ratioP value
All pump repairs completed within 24 hours1237 (5.7)referenceN/Aa
All repairs completed within 48 hours (with some over 24 hours)17123 (13.5)2.36.02
Repairs taking over 48 hours to complete54669 (12.6)2.22.02

aN/A: not applicable.

Cross-Sectional Analysis

The cross-sectional analysis revealed possible predictors of reporting diarrhea. Table 3 shows the odds ratios for diarrhea against other household information gathered during the 2015 survey, along with summary statistics for those characteristics. The quality of dwelling construction was associated with lower reported diarrhea in children, as were having a female head of household and cultivating crops. Apparent risk factors were those related to higher household occupancy and having no regular income. The WASH-related factors of higher per-person water collection and having an improved toilet were apparently protective. Of note, 1.5 jerrycans of water were collected for each household member per day, corresponding to 30-35 liters per person, with few households treating water either by adding chlorine (eg, Waterguard) or by boiling.

Table 3. Bivariate logistic regression analysis of associations of household characteristics with reporting child diarrhea (12% of 840 households) from the survey conducted in March-May 2015.
Household characteristicUnadjusted odds ratio (95% CI)P valuePercentage or mean
Number of repairs0.95 (0.85-1.07).422.7
Repairs within 24 hours0.40 (0.27-0.58)<.00115%
Improved floor0.37 (0.22-0.61)<.00135%
Improved roof0.53 (0.31-0.89).0234%
Improved walls0.52 (0.39-0.71)<.00146%
Improved toilet0.56 (0.38-0.81).00255%
Female head0.65 (0.46-0.92).0139%
Primary religion Islam1.03 (0.71-1.49).1485%
Household head completed secondary school0.96 (0.56-1.63).8730%
Number of people per household1.11 (1.09-1.13)<.0015.4
Sleeping rooms in dwelling0.91 (0.87-0.95)<.0013.1
Number of people per bedroom1.27 (1.26-1.29)<.0012.0
No regular income1.41 (1.18-1.69)<.00143%
Own animals1.08 (0.57-2.06).8135%
Grows crops0.89 (0.67-1.18).4274%
Distance from handpump (m)1.00 (1.00-1.00).64136
Distance from health dispensary (km)0.96 (0.84-1.10).571.8
Distance from nearest market (km)1.05 (1.03-1.06)<.0015.0
Soap observed0.65 (0.36-1.19).1775%
Water treated0.87 (0.38-1.98).7310%
Water storage in the dry season (days)1.10 (0.96-1.27).171.8
Water storage in the wet season (days)1.02 (0.91-1.15).692.7
Number of jerrycans per person per day0.68 (0.64-0.72).0011.53

Multivariable Analysis of Self-Reported Diarrhea

Table 4 presents the adjusted odd ratios (AORs) and 95% CIs of iterative mixed-effects multivariable logistic regression models of child diarrhea: model 1 begins with socioeconomic factors, model 2 introduces a block of dwelling-related factors, and then model 3 introduces a block of WASH-related factors. The protective effect of handpump repairs consistently made within 24 hours remained robust across all multivariable models. Of the socioeconomic factors, having a female head of household (AOR 0.54, 95% CI 0.36-0.82; P=.004) and growing crops (AOR 0.67, 95% CI 0.48-0.95; P=.02) were associated with lower reported diarrhea across all models. Having no income (AOR 1.36, 95% CI 1.11-1.69; P=.003) and being further from the market (AOR 1.10, 95% CI 1.07-1.13; P<.001) were associated with higher odds of child diarrhea. Having more people in the household was also associated with reporting diarrhea (AOR 1.12, 95% CI 1.04-1.21; P=.003), although this was possibly an artifact of aggregating all cases of child diarrhea in the household into a binary variable; nevertheless, an alternate analysis with the number of children in the household produced a similar result. Among the WASH-related factors, having an improved toilet was associated with lower diarrhea (AOR 0.61, 95% CI 0.44-0.84; P=.002). The effect of the dwelling characteristics was less consistent across the three models. As a robustness check, we also refitted these models with errors clustered by pump, rather than by geographical zone, but we observed no substantive differences from the results presented in Table 4.

We built on the full model (model 3) by introducing interaction terms between the following pairs of covariates: having no income and growing crops, a female household head and the presence of soap, and having an improved floor and improved toilet. These interactions are presented in Table 5. Having no regular income and not growing crops was the largest risk factor for reporting diarrhea. Strikingly, if a household was growing crops, it had no additional odds of reporting diarrhea if it had no regular income. Conversely, the benefit of having soap in a household seemed only to accrue to households headed by a woman, in which case the odds of reporting diarrhea reduced substantially. Finally, having an improved floor substantially reduced the odds of reporting diarrhea in households with an improved toilet, but provided no added benefit to those without.

Table 4. Mixed-effects logistic regression models of self-reported diarrhea, adjusted for blocks of covariates, using 2015 household survey data and handpump repair data from 2014 and 2015.
CharacteristicAdjusted odds ratio (95% CI)

Model 1Model 2Model 3
Repairs within 24 hours0.38 (0.24-0.62)0.38 (0.23-0.62)0.34 (0.22-0.52)
Socioeconomic factors

No regular income1.34 (1.12-1.60)1.34 (1.11-1.61)1.36 (1.11-1.69)

Grows crops0.73 (0.50-1.07)0.67 (0.45-0.98)0.67 (0.48-0.95)

People per household1.14 (1.12-1.26)1.15 (1.09-1.20)1.12 (1.04-1.21)

Female head0.63 (0.45-0.89)0.58 (0.37-0.91)0.54 (0.36-0.82)

Distance from market (km)1.06 (1.04-1.09)1.07 (1.03-1.10)1.10 (1.07-1.13)
Dwelling factors

Improved roofa0.65 (0.32-1.30)0.74 (0.38-1.44)

Improved walls0.99 (0.76-1.29)0.99 (0.69-1.42)

Improved floor0.42 (0.21-0.85)0.50 (0.22-1.14)

Number of bedrooms1.03 (0.99-1.07)1.07 (1.04-1.09)
WASHb factors

Improved toilet0.61 (0.44-0.84)

Soap observed0.59 (0.32-1.08)

Jerrycans per person per day0.86 (0.69-1.07)

Water treated0.98 (0.40-2.41)

aNot included in model.

bWASH: Water, Sanitation, and Hygiene.

Table 5. Mixed-effects logistic regression model of self-reported diarrhea with interactions, using 2015 household survey data and handpump repair data from 2014 and 2015.
CharacteristicOdds ratio (95% CI)P value
Main effects

Repairs within 24 hours0.36 (0.24-0.55)<.001

Distance from market (km)1.09 (1.06-1.13)<.001

Improved roof0.73 (0.36-1.48).32

Improved walls0.96 (0.69-1.33).92

People per household1.11 (1.03-1.20).02

Number of bedrooms1.06 (1.03-1.10).02

Jerrycans per person per day0.85 (0.69-1.05).12

Water treated1.01 (0.42-2.46).98
Interactions

Income and crops



Regular income and grows crops1.00 (0.69-1.45).86


No regular income and grows crops1.10 (0.68-1.79).63


No regular income and does NOT grow crops2.30 (1.85-2.86)<.001

Household head and soap



Male head and soap observed0.79 (0.43-1.44).40


Female head and soap NOT observed0.89 (0.62-1.30).41


Female head and soap observed0.32 (0.26-0.38)<.001

Standard of floor and toilet



Improved floor and NO improved toilet0.80 (0.33-1.91).51


Unimproved floor and improved toilet0.72 (0.53-0.98).03


Improved floor and improved toilet0.29 (0.13-0.65)<.001

Principal Findings

This study revealed an association between the speed of pump repairs and child diarrhea morbidity. Only households whose pumps were consistently repaired within 24 hours of a failure reported a significant reduction in child diarrhea. This finding is consistent with modeling work that suggests that even the briefest time without high-quality water can lead to disproportionate health impacts [38,39], but the microbiological pathway very likely does not fully explain the higher likelihood of self-reported illness for pumps that were repaired less rapidly. The lag time between pump failure and survey completion varied considerably, ranging from the day before the survey took place to pumps that were repaired when the maintenance service started over 1 year before the survey look place and had remained functional ever since. In these latter cases, direct microbiological causality between pump downtime and illness is unlikely.

In lieu of the presence of a consistent microbiological pathway, we would propose an additional behavioral explanation. If a household has higher confidence in the reliability of their pump, knowing that mechanical failures will be consistently fixed within 24 hours, they may be less likely to immediately fall back on using lower-quality alternative water sources as they might in the case of an extended pump downtime. If households experience any variability in the speed of pump repairs, then they are more likely to collect, store, and use water from less wholesome alternative sources. These are unlikely to be discarded once the pump is fixed, because there was a time or financial cost in acquiring them, thus raising the potential for ongoing waterborne disease exposure.

In addition to providing evidence that only rapidly repaired handpumps lead to a reduction in child diarrhea, this study highlights other factors that contribute to diarrheal disease in rural households reliant on basic water services. Striking, but unsurprising, are the socioeconomic effects, consistent with the WASH literature: the poorer you are, the more likely you are to experience water insecurity and consequently an increased burden of water-related diseases. Growing crops mitigated the impact of having no income; however, we do not have sufficient information from this study to attribute this to the nutritional benefit of growing food or because it generated occasional income or barter opportunities, either being plausible.

Individual components of traditional WASH interventions and programs did not seem to provide a beneficial health effect when considered in isolation. Our use of interaction terms (Table 5) suggested that soap being available and observed at a home was only associated with a reduction in diarrhea in households headed by women, suggesting that hygiene behaviors in children may be better taught or enforced in households headed by women than by men. Similarly, the benefits of having an improved toilet were magnified by having an improved floor (ie, one made of cement or concrete). Such floors are easier to clean, reducing the likelihood of having human and animal feces present in homes. These empirical data are consistent with conceptual models that articulate a nonlinear relationship between the reduction in fecal contamination and consequent reduction in diarrhea [43,44].

The adaptation strategy of collecting and drinking more unsafe water in response to pump unreliability increases the risk of water-related illnesses. However, this strategy is one that households will rationally stick to unless there is compelling and enduring evidence that it is not necessary. This is consistent with studies on household preferences for rapid pump maintenance [31,34], and was supported anecdotally by conversations with people who were receiving the free repair service. However, even the well-resourced maintenance service linked to this study only fixed 15% of pumps within 24 hours every time they broke down. Acknowledging the possible selection bias in this study, community-managed handpumps are even less likely to be consistently repaired within 24 hours. This is not to discount the many other benefits from reducing pump downtimes, it is simply that health cannot be assumed to be one of them.

From an operational perspective, any pump maintenance service that reduces downtimes by an order of magnitude would be viewed as excellent in the rural water sector or even a best-in-class option. This study demonstrated an association between consistent, rapid handpump repairs and reduced child diarrhea reported in the households that use these pumps, suggesting that such a high level of service may also lead to better health outcomes. Any WASH intervention that achieves a reduction in diarrhea of over 50% would certainly be viewed as a success. If professionalizing handpump operations and maintenance to minimize pump downtimes can yield the health impacts demonstrated in this small study, can it have a substantial impact on the burden of disease?

Only the pumps with the lowest downtimes were associated with this level of health benefit. The 60% reduction in diarrhea was only the best possible outcome for a best-in-class service. The households using handpumps that had received very rapid repair corresponded to only the 15% of pumps where all repairs were completed within 24 hours. An efficacy of 60% translated into an effectiveness in reducing diarrhea morbidity of less than 10% for all the households receiving the repair service. To produce a health benefit, continuity of service must be maintained with near-zero downtime. This level of service is extremely difficult for professional service providers to maintain, and there is scant evidence that community maintenance can consistently achieve these performance levels [24,25,45,46]. FundiFix now operates a hybrid system of reactive and preventative maintenance to maintain pump uptime. Work is underway to use the sensors on the handpumps to monitor the pumps’ condition and predict failures with the aim of eliminating pump downtime altogether [40,47].

Limitations

This study’s primary outcome variable was self-reported diarrhea, with enumerators trained to ask the question according to the WHO definition. Self-reporting is known to have limitations, and diarrhea is a crude proxy for water-related diseases [48,49]. The use of self-reported diarrhea in this study does not in itself call into question the primary finding that consistently rapid repairs are paramount to the delivery of health benefits, but it does mean that caution should be used in interpreting the effect size measured here. As the cross-sectional element of the study was based around one survey, the primary outcome variable was measured at times that varied with respect to the primary exposure. This had advantages for blinding and concealment, but limits the ability to attribute any observed effect to a specific breakdown event. We can only speculate on the extent to which the mechanism for the observed effect is directly biological or behavioral.

Household matching between the two surveys was undertaken rigorously, with unmatched households excluded from analysis where appropriate. The two surveys were 18 months apart and the household characteristics were not necessarily identical during each survey wave. Household composition may have changed with births, deaths, or others joining or leaving the household; household water budgets may also have changed as members transitioned from child to adult roles, or from being breastfed to directly consuming food and water, and other factors.

The exclusion criteria used for this study necessarily restricted the survey to households confirmed to have used pumps that had received repairs from the free maintenance service. The average downtime for handpumps across the study area prior to the trial was 27 days. It is plausible that the communities that chose not to engage with the repair service were those with better repair arrangements and performance prior to the study, introducing a possible selection bias. In addition, the method of household selection was likely to have created a bias toward households living closer to the pump (the average distance from a dwelling to its reference handpump was 136 meters and the maximum was 739 meters). These issues do not affect the internal validity of the study but may reduce external validity and the wider inferences that can be made.

Most of these limitations were the result of using an observational study design, which was linked to establishing the local pump maintenance provider. While the findings may be less widely generalizable, opportunistic operational studies linked to local WASH programs—whether by governments, private operators, or development agencies—have certain benefits. Here, the findings are directly informing the service provider’s operational management of handpumps in this area. By operating within existing and ongoing local programs in this way, findings from such studies can feed directly into local decision-making, and are thus more likely to have an immediate and sustainable impact on local health outcomes [50]. In this case, these findings—already shared with the maintenance service provider—have underscored the importance of reducing pump downtimes to a minimum.

Conclusions

Implicit in the JMP’s definition of “basic water” is the assumption that improved sources of water are of higher quality than unimproved sources and would therefore be associated with the health benefits of lower diarrheal disease morbidity. Our findings suggest that handpumps may only produce health benefits if service delivery can achieve the highest levels of performance, a level of performance difficult to maintain even under ideal operational circumstances. These findings provide empirical support to prior modeling of the relationship among water service reliability, water quality, and health, which suggests that even short periods of supply intermittency may have large adverse health impacts [38,39].

The required consistent reduction in downtimes needed is a challenge for even FundiFix, a well-resourced and tightly managed service provider that achieves higher uptimes than are typical in the sector. Our findings have implications beyond handpumps and are potentially relevant to other forms of basic water service. For these, the management arrangements are often limited, back-up sources are most likely from an unimproved source, and similar household choices will have to be made in response to an unreliable supply. This underscores the need to pursue on-premises, continuous supply.

These findings are also consistent with a rich literature linking water-related diseases to poverty. We found that socioeconomic factors were more closely linked to household disease than some classic WASH factors, which taken in isolation did not reduce the incidence of child diarrhea. This implies that WASH interventions will be more effective when integrated into wider antipoverty and service delivery efforts, rather than implemented in isolation. Both of these findings support the current direction of the WASH and Water Security research agenda, which considers the key role water plays in other fields such as education and nutrition, and emphasizes the wider systems of service delivery, governance, and rights of which WASH interventions are a part [51,52].

Acknowledgments

The authors thank Said Banje, Tim Foster, Nancy Gladstone, Susie Goodall, Rob Hope, Alan Howard, Jacob Katuva, Johanna Koehler, Idd Mwaropia, James Okoti, and Amber Pearson for their support, as well as Rural Focus Ltd and the Kwale County Government. This work was supported by the following grants: “New Mobile Citizens and Waterpoint Sustainability in Rural Africa” (ESRC, ES/JO18120/1) and “Groundwater Risk Management for Growth and Development” (NERC, NE/M008894/1), funded by the UK Economic and Social Research Council (ESRC) and the UK Natural Environment Research Council (NERC)/UK Department for International Development, respectively, along with the Household Water Insecurity Experiences (HWISE) Research Coordination Network, funded by the US National Science Foundation (BCS-1759972).

Data Availability

The full data analyzed for this study are not publicly available in order to maintain the confidentiality and anonymity of the participants. The publicly available data, which were generated during UK Research and Innovation–funded projects ES/JO18120/1 and NE/M008894/1, are available in the UK Data Service repository [53].

Authors' Contributions

PT and DJB developed the study concept and design. PT, JS, and MB analyzed the data. PT wrote the manuscript in consultation with JS and DJB. All authors discussed the results and contributed to and agreed on the final manuscript.

Conflicts of Interest

PT is an unpaid trustee of FundiFix Water Services Trust, the organization spun out from this research project of which this study is a part. The other authors have no connection to FundiFix and no conflicts to declare.

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AOR: adjusted odds ratio
DALYs: disability-adjusted life years
JMP: Joint Monitoring Programme
SDG: Sustainable Development Goal
UNICEF: United Nations Children's Fund
WASH: Water, Sanitation, and Hygiene
WHO: World Health Organization


Edited by A Mavragani; submitted 08.09.22; peer-reviewed by A Krishnan, X Ma, KK Yadav, P Chintalapati; comments to author 25.08.23; revised version received 23.10.23; accepted 14.12.23; published 16.01.24.

Copyright

©Patrick Thomson, Justin Stoler, Michelle Byford, David J Bradley. Originally published in JMIR Public Health and Surveillance (https://publichealth.jmir.org), 16.01.2024.

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