Improving sanitation conditions in low-income communities is a major challenge for rapidly growing cities of the developing world. The expenses and logistical difficulties of extending sewerage infrastructure have focused increasing attention on the requirements for safe and cost-effective fecal sludge management services. These services, which are primarily provided by the private sector, include the collection and treatment of fecal waste from latrine pits and septic tanks. To determine the degree to which market forces can promote safe fecal sludge removal in low-income neighborhoods of Kisumu, Kenya, we compared household willingness-to-pay for formal pit emptying with the prices charged by service providers. Through surveys of 942 households and a real-money voucher trial with 646 households, we found that stated and revealed demand for formal emptying services were both low, with less than 20% of households willing to pay full market prices. Our results suggest that improving fecal sludge management in these neighborhoods via the private sector will require large subsides, ranging from 55.1–81.4 million KES (551,000–814,000 USD) annually, to address the gap between willingness-to-pay and market prices. Raising and administering subsidies of this scale will require the development of a city-wide sanitation master plan that includes investment, management, and regulatory procedures for fecal sludge management. In the absence of government investment and coordination, it is unlikely that the private sector will address safe sanitation needs in low-income areas of Kisumu.
Citation: Peletz R, MacLeod C, Kones J, Samuel E, Easthope-Frazer A, Delaire C, et al. (2020) When pits fill up: Supply and demand for safe pit-emptying services in Kisumu, Kenya. PLoS ONE 15(9): e0238003. https://doi.org/10.1371/journal.pone.0238003
Editor: Khin Thet Wai, Ministry of Health and Sports, MYANMAR
Received: March 13, 2020; Accepted: August 7, 2020; Published: September 3, 2020
Copyright: © 2020 Peletz et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Data Availability: The data are available at doi.org/10.17632/6w49x86k6y.1.
Funding: This research was delivered through a research agreement between Water & Sanitation for the Urban Poor (WSUP) and The Aquaya Institute. The agreement was funded under the Urban Sanitation Research Initiative managed by WSUP and supported by UK Aid from the UK government.
Competing interests: The authors have declared that no competing interests exist.
Residents of low-income, urban settlements in developing countries generally do not have access to formal, regulated fecal sludge management (FSM) services, which primarily target middle- and high-income households that can afford market prices . FSM in poor neighborhoods commonly includes unsafe practices, including the employment of informal manual emptiers who remove fecal sludge by hand and dispose of it in the surrounding environment. These practices pose environmental and health risks to households and emptiers, who often operate without proper equipment, training, or oversight [2–4]. As a result, inadequate sanitation service provision disproportionately affects the health and environment of the urban poor: a 2010 study of sanitation subsidies in six low-income countries found that that the majority of poor households pay high costs for onsite sanitation, an activity seen as a private good and a household responsibility, despite the negative public health externalities of poor sanitation .
Safe emptying services are inevitably more expensive than informal practices due to licensing requirements, the costs of transporting fecal sludge to designated disposal areas, and dumping fees . Studies in different settings have found that that the willingness-to-pay (WTP) for safe latrine emptying services among low-income households is substantially lower than market prices: for example, in rural Bangladesh household contributions covered approximately 47% of service provider costs , and in urban Rwanda, affordable price points only covered approximately 40% of service provider costs for formal manual emptying . Quantifying the differences between market prices (supply) and household WTP (demand), and, thereby, the extent to which low-income customers can bear the cost of safe emptying, is central to designing appropriate service delivery and financing approaches.
Various approaches, however, are emerging to subsidize sanitation for the poor, particularly in urban settings. In Dhaka, Bangladesh, for example, the SWEEP fecal waste collection service is implementing an internal cross-subsidy mechanism to serve the poor. Customers in low-income areas are charged less than middle/high-income customers, and, after achieving commercial viability in mid-2017, SWEEP must now ensure that 30% of customers are actually classified as low-income based on two parameters: their geographic location in a low-income area and confirmation of income status by customer . Financial modeling indicates that a 70–30% mix of high-income/institutional and low-income customers will ensure sufficient profit to maintain private-sector interest in the service delivery partnership. Sanitation surcharges that are levied on top of utility customer charges provide another strategy for subsidizing the provision of sanitation services and infrastructure . In Africa, at least six cities have implemented a sanitation surcharge, and in three of these cities (Lusaka, Zambia; Bobo-Dioulasso, Burkina Faso; and Ouagadougou, Burkina Faso) the resulting revenues are earmarked for pro-poor services . As of 2010, the surcharge in Burkina Faso had supported improved sanitation infrastructure for nearly one million people, without additional donor inputs . By 2012, the surcharge in Lusaka had raised at least $2 million, and disbursements had funded 200 onsite sanitation facilities and condominial sewerage in low-income peri-urban areas .
Other pro-poor sanitation improvement efforts address the costs of service provision. In Dakar, Senegal for example, the national sanitation agency ONAS (Office National de l’Assainissement du Sénégal) trained and certified private operators and created a call center to coordinate mechanized emptying services. The call center collects bids from vacuum truck operators for emptying jobs, which, reportedly has lowered prices by 20% and promoted increased use of vacuum trucks in low-income areas of the city . Low-cost emptying technologies are also emerging: the Gulper, a manually operated latrine emptying pump designed for densely populated urban areas is now one of the most common manually-driven systems for removing fecal sludge in Africa; similarly, the Vacutug is a self-propelled mechanized vacuum pump successfully introduced in low-income areas of Nairobi, Kenya, and in Dar es Salaam, Tanzania [11,12].
Additional FSM innovations combine technology development with new service delivery models at household and community levels. For example, multiple organizations (such as SOIL in Haiti, Sanivation in Naivasha, Kenya, and Clean Team in Kumasi, Ghana) support the development and use of container-based sanitation (CBS) technologies for households. Container-based toilets collect fecal waste in a sealable, removable receptacle for subsequent transport to a treatment facility . Sanergy has established a franchise system for community-level CBS in a low-income area of Nairobi, Kenya . In these cases, treated and processed fecal waste is sold (e.g., as fertilizer, an energy source, or animal feed) to offset fecal sludge collection and processing costs.
Finally, pro-poor sanitation programs continue to include the development of sewerage options. The Kenya Informal Settlements Improvement Project (KISIP) financed the expansion of sewer connections in two low-income areas in the city of Kisumu . Also in Kenya, the Nakuru Water and Sanitation Services Company, the water and sewerage utility for the city of Nakuru, partnered with WSUP to construct a sewer network in one of the city’s low-income areas . In Brazil, condominial sewerage systems connect housing blocks to small dispersed treatment facilities, thereby reducing the need to build and maintain larger-scale traditional infrastructure .
To support sanitation improvements in Kisumu, the third largest city of Kenya, we measured the gap between market prices and WTP for safe emptying services in the city’s low-income areas. Stated and revealed willingness-to-pay (WTP) methods provide options for quantifying demand for improved sanitation products and services among low-income households. Stated WTP methods generally use household surveys to assess demand for hypothetical products and services by asking respondents to reflect on price points through a series of questions [1, 17–19]. In contrast, revealed WTP methods obtain results from real money price-responses (i.e., market data or experiments)  and are generally considered more reliable because they reflect respondents’ actual (rather than hypothetical) purchasing behaviors . Our study, therefore, addressed the following objectives: 1) to compare household demand for safe emptying services with the prices charged for these services; and 2) to compare stated and revealed WTP by conducting both household surveys and a real-money voucher experiment.
Kisumu is Kenya’s third largest city with an estimated 419,000 inhabitants in its urban constituencies, of which approximately 60% live in low-income areas [20, 21]. Approximately 20% of households are connected to the sewerage network that transports waste to two treatment facilities operated by the local utility, Kisumu Water and Sewerage Company (KIWASCO) . An estimated 70% of households use pit latrines, and 5% use septic tanks, primarily in middle- and high-income households . Only 33% of Kisumu’s fecal waste (sewage and fecal sludge) is safely managed, mostly via treatment at KIWASCO’s fecal sludge treatment site . In Kisumu’s low-income areas, it is common for informal manual pit emptiers to dispose of fecal waste in nearby waterways or bury it onsite .
Our study design comprised two phases. From May to November 2018, we conducted a market assessment to identify existing emptying services in Kisumu and to document barriers that prevented safe pit-emptying services from operating in low-income areas. From February to June 2019, we conducted a household survey and real-money voucher trial to evaluate the WTP of Kisumu’s low-income residents for safe pit-emptying services by licensed operators that removed and transported fecal sludge for offsite treatment.
Our market assessment included the following activities: i) literature review of national and county-level policy and program documents relevant to sanitation; ii) in-depth interviews with key water and sanitation stakeholders; iii) pit emptying observations; iv) transect walks in low-income areas; and (v) focus group discussions with low-income residents (Fig 1). Our literature review examined national strategies and policies, the county’s draft sanitation policy, and documentation on county and city sanitation programs. We interviewed multiple stakeholders in Kisumu’s sanitation sector using a ‘snowball’ method , whereby we started with contacts at Water and Sanitation for the Urban Poor (WSUP), an international non-governmental (NGO) organization implementing programs in Kisumu, and KIWASCO who subsequently referred us to other stakeholders. These informants included additional KIWASCO staff, municipal and county government officials, microfinance institution representatives, NGO workers, and fecal sludge emptying service providers. The fecal sludge emptying service providers included vacuum truck operators (VTOs), informal manual emptiers, and “formal” manual emptiers; we defined formal manual emptying as trained emptying groups that worked with recognition of the local government and National Environment Management Authority (NEMA), had permission to dump waste at the city’s treatment facility, and complied with public health regulations. We observed pit emptying by these service providers to understand their current operating processes. We also conducted transect walks to document contextual characteristics of the neighborhoods where they operated, such as access to water and sanitation services, geological and infrastructure conditions, typology (urban, peri-urban, rural) and land tenure (private versus government housing). Additionally, we held Focus Group Discussions (FGDs) in several low-income areas to understand sanitation and emptying preferences and challenges. We recruited FGD participants through local leaders (e.g., local village elders or chiefs) identified through WSUP and held separate FGDs for persons with disabilities and women. We conducted interviews and FGDs in either the local languages (Swahili and Luo) or English; we took detailed notes in English. We conducted interviews, emptying observations, and FGDs until we reached saturation (i.e., no new information was obtained with additional data collection).
Pit-emptying stakeholders and service providers
The Kisumu County Government and the National Environment Management Authority (NEMA) are the main official bodies responsible for sanitation policy implementation and regulation in the city of Kisumu. At the county level, NEMA is responsible for monitoring environmental impact assessments and effluent discharged into sewerage systems . The Kisumu County Government ensures that public health standards are met and is responsible for licensing VTOs. In practice, however, NEMA and the city Public Health department facilitate VTO licensing. KIWASCO is the sole utility providing water and sewerage services in the city of Kisumu. NGOs also play a role in the provision of sanitation facilities and services. WSUP, for example, developed standard operating procedures for safe fecal sludge management and supported Kisumu County in the development of the Environmental Sanitation and Hygiene Policy. WSUP also trained Gasia Poa, one of the three formal manual pit-emptying groups that primarily operate in low-income areas of Kisumu city, on safe emptying practices in 2018 (Table 1). Gasia Poa has established a licensing agreement with the County Public Health Office and is allowed to dispose of fecal waste at KIWASCO wastewater treatment facilities free of charge. Another program, KisumuSan (2016–2021), led by Practical Action, trained the two other manual emptying groups (Vukasasa in the Nyalenda low-income area and BlueStars in the Obunga low-income area) and provided each group with a portable mechanized emptying device called a Gulper (Table 1). During our study period, eight vacuum trucks were operating in Kisumu City: KIWASCO owned two vacuum trucks and the remaining six were privately owned. Only four of the vacuum trucks (two from KIWASCO and two that were private) were licensed by NEMA. Finally, informal, unlicensed, manual emptiers also commonly operate in low-income areas of Kisumu city, though typically at night to avoid penalties . Table 1 describes the different emptying groups with their respective price structures.
Table 2 summarizes the characteristics of survey respondents and those eligible for vouchers. We conducted surveys with 942 households and allocated vouchers to 646 (69%) of these households (Fig 1). Characteristics were generally similar between survey respondents and the subset of the population that were eligible for vouchers (Table 2). Approximately half (53%, 500/939) of the respondents had at least some secondary education. The majority of respondents (75%, 704/942) were landlords or homeowners, due to our sampling strategy targeting this population, which is described in the Methods section 2.4.3. Households had a median of five members and 42% (392/942) had a least one child under five years of age. When asked about their monthly household income ranges, 29% (258/892) of households reported <7,000 KES (70 USD), and 23% (206/892) of households reported 7,000 to <10,000 KES (70 to <100 USD), indicating that at least half of the population was living on less than 100 KES (1 USD) per person per day. The median time living on the compound was 18 years.
Most households (74%, 698/942) had dry improved pit latrines; the remainder (19%,176/942) primarily had pour-flush toilets connected to some form of underground containment (Table 2). Most toilet facilities (85%, 801/942) were shared, serving a median of six households. Other reports note that across the entire city, approximately 30% of households share toilets . Landlords/homeowners almost always paid for their own latrine construction (99%, 699/704) and tenants rarely paid for latrine construction (5%, 34/733). Piped water supplied by KIWASCO was the primary drinking water source for most households: either via household taps (44%), neighbor or shared connections (30%), or public taps (20%).
We found that 40% (374/942) of households had emptied their underground containment at least once within the past 12 months, and 16% (147/942) had emptied in the past three months (Table 2). FGD respondents noted that some households emptied their underground containment as often as every one to two months, especially during the rainy season and in areas with high water tables, where pits are usually shallow (approximately 1.2–2.4 m) and fill up quickly; flooding, which is common in low-income areas in the east of Kisumu (such as Nyalenda and Manyatta), also increased pit-emptying requirements.
Household survey respondents reported paying a median of 3,000 KES (30 USD) for a single emptying, including solid waste removal (Table 2). Most households (62%) employed informal manual emptiers, though 28% of households contracted with an operator of a small vacuum truck (<7 m3) (Table 2). In both household surveys and FGDs, respondents reported that they did not use formal manual emptiers because they were unfamiliar with the service. Respondents reported not using VTOs because they perceived that VTO services were too expensive, could not access their latrines, and/or would not empty pits that contained solid waste. Approximately half of tenants (53%, 67/126) paid for their own containment emptying (Table 2).
We conducted the household surveys and voucher trial in eight low-income areas of Kisumu (Bandani, Manyatta A, Manyatta B, Nyabera, Nyalenda A, Nyalenda B, Nyamasaria, and Obunga) . These eight areas met the following criteria for the household surveys: i) located within urban Kisumu (including Central, East, and West constituencies); ii) classified as urban (i.e., not peri-urban or rural) as observed during transect walks; iii) did not have government housing according to local sources (i.e., KIWASCO, WSUP); and iv) had a limited number of sewer connections (estimated <20% coverage).
We measured WTP for two existing safe pit-emptying services: i) Gasia Poa, a formal manual emptying group trained by WSUP that deployed emptiers equipped with safety gear to manually transfer waste from pit latrines and septic tanks to large barrels; and ii) VTOs that used exhauster trucks to suction fecal waste from pit latrines and septic tanks. Both services transported fecal sludge to one of KIWASCO’s treatment sites and were licensed by the local authorities. Gasia Poa also provided manual emptiers with vaccinations against infectious diseases and protective gear/equipment to avoid direct contact with fecal sludge. We explained these emptying services to study participants with detailed graphics (S1 Fig). We did not measure WTP for informal manual emptying because the price that study households paid for informal emptying was well established at 1,000–3,000 KES (Table 2).
We randomly selected households to participate in our surveys, which collected data on household demographics, socioeconomic status, water and sanitation access, and WTP for emptying services. We used ArcGIS (ESRI, Redlands, CA, USA) to randomly select a number of GPS coordinates proportional to each low-income area’s total population . Survey enumerators navigated to each GPS coordinate and identified the nearest compound. Subsequently, they interviewed one landlord or homeowner in the compound, if available, and a single tenant (if multiple tenants were present, the enumerator selected the first one on the left side of the compound). Enumerators continued surveying all compounds in one designated direction until they reached a maximum of five surveys per day (four landlords or homeowners and one tenant). We designed this sampling strategy so that approximately 80% of respondents were landlords or homeowners and 20% were tenants, because the financial responsibility for emptying generally falls on landlords and homeowners (i.e., tenants typically depend on landlords to pay for emptying) . Households were eligible to participate in the household survey if they: i) were exclusively a residence (not a business or institution); ii) had an adult (≥18 years) head of household; iii) had an onsite sanitation facility that required emptying; and iv) were accessible to emptying by service providers. Additionally, only landlords that lived on the premises were eligible to participate. If a head of household was not available during the initial visit, the enumerators returned to the household at least two more times before classifying the household as not available. The questionnaire was administered in the local language, Luo (S1 and S2 Texts).
WTP estimates obtained through surveys are referred to as stated preferences . Our household survey employed the double-bounded dichotomous choice method to measure stated WTP for pit-emptying services . We first asked respondents to provide a “yes/no” answer to two closed-ended price probes [18, 28] (Fig 2). If the respondent answered “yes” to the first question, we then queried their willingness to pay a higher price. Alternatively, if the respondent answered “no” to the first question, we then queried their willingness to pay a lower amount. Providing a sequence of questions motivates respondents think about a relevant price range [1, 18, 19], and other studies of WTP for water and sanitation products and services have applied similar dichotomous choice methods [6, 8, 19, 28, 29]. We followed the dichotomous choice questions with an open-ended question asking respondents to state the highest amount they would be willing to pay . We report this maximum WTP as “stated WTP” in the rest of the paper.
Using the double-bounded dichotomous choice method, we randomly asked households (i.e. landlords/homeowners and tenants) if they were willing to pay 3,000/6,000/8,000/11,000 KES (30/60/80/110 USD) for Gasia Poa emptying services. Depending on whether the respondent answered positively or negatively to the randomized amount, we then asked participants the same question for the next higher or lower amount. For example, if a respondent was willing-to-pay 6,000 KES (60 USD), we then asked if she was willing-to-pay 8,000 KES (80 USD), followed by an open-ended question about their maximum WTP. We used the same method to assess WTP for VTO emptying services with different starting price points.
In each survey, we randomized the starting price points for the double-bound dichotomous choice questions (Fig 2). We established these price points at approximately 20%, 40%, 60% and 80% of market prices of emptying services (rounding to the nearest 500 or 1,000 KES); we estimated market prices to be 14,000 KES (140 USD) for Gasia Poa (inclusive of an additional fee for solid waste removal), 6,000 KES (60 USD) for VTO emptying of dry pits, and 4,000 KES (40 USD) for VTO emptying of wet pits or septic tanks. As a result, our randomized starting price points were: 3,000/6,000/8,000/11,000 KES (30/60/80/110 USD) for Gasia Poa emptying services; 2,000/3,000/4,000/5,000 KES (20/30/40/50 USD) for VTO emptying of dry pits; and 500/1,500/2,500/3,500 KES (5/15/25/35 USD) for VTO emptying of wet pits. We used the VTO price points for wet pits if households had flush/pour flush latrines; otherwise, we used the dry pit price points. We queried all respondents regarding WTP for both Gasia Poa and VTO emptying services.
We also asked all respondents about their WTP for subscription emptying services for Gasia Poa and VTOs, as an alternative to large one-time household outlays. We presented these subscription services as twelve monthly payments that would cover one emptying service during the twelve-month period, at the time of the subscriber’s choice. Prior studies have demonstrated that tenants’ demand for water and sanitation services is reflected in rent premia [22, 31, 32]. Therefore, when surveying tenants, we asked about their WTP for an increase in rent (rather than WTP for one-time outlay or subscription services) if emptying services were provided when necessary in their dwelling. Our starting price points for rent increases were 50/100/200/300 KES (0.5/1/2/3 USD) per month, for both Gasia Poa and VTO services.
Results obtained from real money price-responses (i.e., market data or experiments) are often referred to as revealed preferences . Following the household survey, we conducted a real-money sales trial to estimate revealed WTP for the two types of emptying services. To conduct our sales trial, we randomly distributed vouchers that provided discounted prices for pit-emptying services to eligible households. Subsequently, we tracked voucher redemption rates at each discount level to estimate WTP at different price points (Fig 1). We selected households for the real-money sales trial if they responded to the household survey, they reported that they were financially responsible for pit emptying, and their pit would likely require emptying at any time within three months of the survey. We classified households as likely to require pit emptying within the next three months if they met any of the following criteria: (i) they reported that they intended to empty their pit in the next three months, (ii) enumerators observed that fecal sludge was within one meter from the top of the pit, (iii) there were at least 25 households living in the same compound, (iv) their underground containment had not been emptied within the last two years, or (v) they were living in a high-water-table area and had lived there less than one year (and therefore were presumably unaware of the frequency of emptying needed); 97% of our study population met the first or second criteria. We selected the three-month time frame based on our market assessment results: households reported emptying underground containment every one or two months in areas with high water tables and every six months in areas with low water tables.
We provided eligible households with a discount voucher for either VTO or Gasia Poa emptying services based on the following factors: households were eligible for Gasia Poa vouchers if their superstructure and slab were stable enough to support Gasia Poa emptying methods, and households were eligible for VTO services if they were located within 50 meters of a road. Households eligible for both Gasia Poa and VTO services randomly received a voucher for one of the two services. As previously noted, we also classified VTO services as wet (vs. dry) if they had flush/pour-flush latrines; the VTOs verified this classification and pit latrine accessibility before vouchers were distributed. If multiple latrines were eligible for emptying within a single household compound, enumerators asked the respondent to select one latrine for emptying with the discount voucher.
We established the voucher price points at approximately 20%, 40%, 60% and 80% of market prices of emptying services (rounding to the nearest 500 or 1,000 KES); we estimated market prices to be 14,000 KES (140 USD) for Gasia Poa (inclusive of an additional fee for solid waste removal), 6,000 KES (60 USD) for VTO emptying of dry pits, and 4,000 KES (40 USD) for VTO emptying of wet pits or septic tanks. As a result, the discounted voucher price points were: 3,000/6,000/8,000/11,000 KES (30/60/80/110 USD) for Gasia Poa emptying services; 2,000/3,000/4,000/5,000 KES (20/30/40/50 USD) for VTO emptying of dry pits; and 500/1,500/2,500/3,500 KES (5/15/25/35 USD) for VTO emptying of wet pits. The vouchers included a household identification number, a phone number for the pit-emptying service, the estimated market price for the specified service, the discount amount that the household received, and their expiration date (S2 Fig). We instructed households that they should not exchange vouchers with other households, and we marked eligible latrines with stickers specifying the service provider’s name and contact details. Households had approximately two to four months to redeem vouchers before their expiration on June 6, 2019.
To redeem their discount vouchers, households had to call a phone number on the voucher to coordinate the pit-emptying service. Households paid for their discounted emptying services via the mobile money application M-Pesa. To monitor services provided in return for voucher redemptions, we attended 71% (85/119) of the emptying jobs. We reimbursed pit emptier groups the difference between the market price of the emptying service and the discount voucher amount.
In July 2019, approximately 3–5 months after discount voucher distribution, we conducted follow-up surveys with approximately 20% of the households that received discount vouchers. We stratified this sample by voucher redemption so that 50% of follow-up survey respondents redeemed their vouchers (Fig 1). Within each stratum, we randomly selected a subset of households for follow-up using Excel.
Our target sample size was 300 vouchers per emptying service, or 75 vouchers per price point (600 vouchers total). This sample size allowed us to detect a minimum 22 percentage-point difference in the proportion of the population willing to pay for the two different services at each price point.
During our market assessment, we analyzed our interview notes for common themes and triangulated information from key informant interviews, FGDs, and pit emptying observations. We entered household survey responses into the CommCare survey and data management application (DiMagi Inc., Cambridge, MA USA) on mobile phones (Samsung Galaxy J4, South Korea). We conducted quality control checks on 10% (95/942) of surveys: 4.6% (43/942) spot checks and 5.5% (52/942) back checks. When calculating revealed WTP, we classified households that were eligible for vouchers but refused their randomly allocated discount voucher as not willing to pay the voucher price (5%, 31/646 households) (Fig 1). We categorized participating households into socioeconomic status quintiles using an asset index and principle component analysis . To generate customer demand curves, we used the cumulative percentage of respondents willing to pay for emptying services at different prices. To compare WTP for monthly subscription vs. one-time payments, we adjusted the 12 monthly payments to their net present value using a discount rate of 10%. To examine factors associated with WTP, we conducted bivariate analyses of mean stated WTP using sample t-tests for binary variables and an analysis of variance (ANOVA) for categorical variables (e.g., wealth quintiles and education levels). We also examined factors associated with WTP in multivariate models using maximum likelihood functions for the double-bound dichotomous choice method . To examine factors associated with voucher redemption, we conducted bivariate and multivariate analyses using logistic regression. For all types of multivariate models, we included all factors with bivariate associations with a significance value of p<0.1. We tested for collinearity by computing the condition index from the correlation matrix and excluded variables if their condition index was >10 . Furthermore, we compared WTP data for stated and revealed preferences using a linear regression model controlling for the survey or voucher price point. We analyzed quantitative data using the statistical package Stata 15 (StataCorp, College Station, TX). We used the following exchange rate for the analysis: 100 KES to USD 1.00 (June 6, 2019, oanda.com).
Financial requirements for expanding safe emptying services
Approximately 62% of Kisumu’s population, or 51,965 households, currently lack safe emptying & transport services . Even with the projected sewer expansion to an additional 20% of households , 42% of the population, or an estimated 35,202 households, will continue to require safe emptying & transport services in the near- to mid-term future (S1 Table). Using data from our market assessment and household surveys, we estimated the financial requirements for serving these households, both in terms of capital requirements and operational costs under two scenarios: with and without the projected sewer expansion. All assumptions and step-by-step calculations are provided in S1 Table. In particular, we assumed that 75% of toilets would be serviced by VTOs and 25% by formal manual emptiers, based on a complementary study in which we assessed the expansion potential of both services in Kisumu’s low-income neighborhoods . To calculate capital expenditures (CAPEX), we estimated the number of exhauster trucks, pick-up trucks and tractors required to serve an additional 35,202 or 51,965 households, depending on the scenario (S1 Table). We approximated operational expenditures (OPEX) using average market prices, which capture capital depreciation and possible service provider margins. To estimate household subsidy requirements, we compared OPEX to the amount that approximately 80% of households were willing to pay for safe emptying services (S1 Table). We verified that this amount was consistent with current market prices for informal manual emptying (Table 1).
Research approvals and ethical review
The Western Institutional Review Board (WIRB) (Puyallup, WA, USA) determined this study exempt from full ethical review under 45 CFR §46.101(b)(2) of the Federal Common Rule in the USA. In Kenya, we obtained ethical approval for our research from Amref Health Africa (AMREF) (ESRC P493/2018) and a research permit from the National Commission for Science, Technology, and Innovation (NACOSTI) (NACOSTI/P/19/39980/28701). We provided all participants with verbal and printed details of the study in the local language. We also obtained informed written and verbal consent from all participants.
Stated WTP from household survey
Stated WTP was higher for Gasia Poa services than for VTO services (Fig 3A). Median stated WTP was 3,000 KES (30 USD) for Gasia Poa services (mean = 3,438 KES; 34 USD), representing approximately 25–43% of market prices (which ranged from 7,000–12,000 KES, 70–120 USD). Less than 20% of respondents were willing to pay the lower-bound market price of 7,000 KES (70 USD) (Fig 3A). Median stated WTP was 2,000 KES (20 USD) for VTO services (mean = 2,182 KES, 22 USD), representing approximately 33–50% of market prices (which ranged from 4,000–6,000 KES, 40–60 USD). 14% of respondents had a stated WTP of 4,000 KES (40 USD), the lowest market price for VTO services (Fig 3A).
(a) Stated WTP for Gasia Poa and VTOs (n = 942), (b) Stated and revealed (voucher) WTP for Gasia Poa (n = 646), (c) Stated and revealed (voucher) WTP for VTOs (n = 646), (d) Stated WTP for monthly subscription services for Gasia Poa (n = 795) and VTOs (n = 796) (e) Stated WTP for Gasia Poa comparing one-time and subscription services (n = 795), (f) Stated WTP for VTOs comparing one-time and subscription services (n = 796), and (g) Stated WTP for additions to rent (n = 145). Exchange rate of 100 KES = 1 USD (oanda.com, June 6, 2019).
Revealed WTP from voucher trial
Households redeemed 119 vouchers, which represented 11% (38/350) of the vouchers distributed for Gasia Poa emptying services and 27% (81/296) of the vouchers distributed for VTO emptying services (Fig 1). Revealed WTP was lower than stated WTP for both Gasia Poa and VTO services at every price point; however, for Gasia Poa services, this difference was not statistically significant across the comparable price range (p = 0.17) (Fig 3B). We did not provide Gasia Poa vouchers at prices under 3,000 KES (30 USD) and, therefore, we were unable to compare revealed and stated demand at prices lower than this amount (Fig 3B). With respect to VTO services, the proportion of respondents that redeemed discount vouchers was 39 percentage points less than the proportions that stated they would pay those amounts during our surveys (p<0.01) (Fig 3C).
WTP for subscription services and rent increases
Based on the household survey data, we determined that demand for a VTO service subscription ranged from 52% of respondents willing to pay 200 KES (2 USD) per month to 6% of respondents willing to pay 500 KES (5 USD) per month (Fig 3D). Stated WTP for a subscription fee was again higher for emptying services provided by Gasia Poa, ranging from 44% of households willing to pay 300 KES (3 USD) per month to 12% of households willing to pay 700 KES (7 USD) per month (Fig 3D). Across price points, we did not find substantially higher stated WTP among households when comparing the annual (12-month) sum of monthly subscription payments (using net present value) with one-time services payments for either emptying by VTOs or Gasia Poa (Fig 3E and 3F). However, when we asked respondents if they preferred a 12-month subscription service compared to a one-time payment, 61% (487/942) reported that they preferred the subscription (38% preferred the one-time payment and 1% preferred a combination of the two).
Tenant willingness to increase rent payments to cover safe emptying services was almost identical for VTO and Gasia Poa services (Fig 3G). The median maximum increase that respondents stated being willing to pay was 100 KES (1 USD) per month for both services. At an increase of 50 KES (0.5 USD) per month, 90% of tenants were willing to pay for VTO or Gasia Poa services. At 100 KES (1 USD) per month, 78% were willing to pay for Gasia Poa and 80% for VTOs; at 300 KES (3 USD) per month, the proportion dropped to 23% for Gasia Poa and 20% for VTOs (Fig 3G). For comparison, tenants reported paying a median rent of 3,000 KES (30 USD) per month.
Factors associated with WTP
Bivariate and multivariate model results showed that male and younger survey respondents were willing to pay significantly more for both types of emptying services (S2 Table and S3 Table, all p<0.05). In the multivariate models, survey respondents had a significantly higher stated WTP for Gasia Poa services if they reported sharing a latrine (p = 0.03) and were more educated (p = 0.03) (S3 Table). Survey respondents had a significantly higher stated WTP for VTO services if they were wealthier (p<0.01), were tenants (p<0.01), and had a toilet located less than 50 m from a road (p<0.01) (S2 Table and S3 Table). With respect to voucher redemption, we found that respondents were significantly more likely to redeem their vouchers if they were wealthier (p<0.01) and received a higher discount voucher (p<0.01) (S4 Table).
To obtain customer feedback, we conducted follow-up surveys with 119 households that received vouchers: 59 households that redeemed their vouchers and 60 that did not redeem. We found that most households that redeemed their vouchers were satisfied with the emptying service: when asked if they would use the same service again, 84% of households responded positively (Table 3). When asked about future emptyings, 54% of households reported that they planned to use VTOs, and 46% planned to use a formal manual emptying group; most households chose the service they had used through voucher redemption and none of the households reported plans to use informal manual emptiers (Table 3). When asked what they liked about the emptying services, common responses were that the service had minimal smell (51%), no spillage (34%), solid waste removal (32%), proper sludge disposal (32%), and/or the entire pit was emptied (29%) (Table 3). When asked what they disliked about the service, common responses were that their pits were not fully emptied (19%), the service was too costly (12%), or solid waste was not removed (10%) (Table 3).
Among households that did not redeem their emptying vouchers, the main barriers for voucher redemption that they reported were lack of money (25/60, 42%) or high price (15/60, 27%). Ten households (17%) reported that their pits did not require emptying, though five of these households also listed lack of money or high price as barriers. Other reasons (all reported by fewer than five households) were that households were not sure how to redeem their vouchers, had difficulty scheduling the service, were waiting for the service provider to follow up, had plans to upgrade their latrine, lost their voucher, or lived near road construction that made the household inaccessible. Fifteen of the households that did not redeem their vouchers (25%) reported using another service to empty their pit in the past three months: nine reported using informal manual emptiers, four reported using VTOs, and two reported using one of the formal manual emptying groups.
Financial requirements for expanding safe emptying services
To expand formalized fecal sludge emptying and transportation services to the approximately 51,965 households of Kisumu that are currently underserved (corresponding to approximately 8,661 toilets), we estimated that the required capital investment would amount to 84 million KES (840,000 USD) for the purchase of eight exhauster trucks, seven pick-up trucks and one tractor (S1 Table). In addition to these capital investments, ensuring universal access to safe emptying services would require bridging the gap between markets prices and WTP for operational expenses. Assuming that a toilet is emptied on average once per year, we estimated annual costs of 5,000 KES (50 USD) per toilet served by VTOs, and 9,500 KES (95 USD) per toilet served by formal manual emptiers (S1 Table). Serving the additional 8,661 toilets would thus require operational expenditures of 53 million KES (530,000 USD) annually (S1 Table).
Our survey data showed that the first quintile of WTP (the amount that 80% of households stated being willing to pay) was 1,200 KES (12 USD) for VTO services and 2,100 KES (21 USD) for formal manual services. Extrapolating to the 8,661 toilets requiring safe emptying and transport services in Kisumu, we estimated that cumulative WTP would amount to 12.3 million KES (123,000 USD) annually, corresponding to 23% of operational costs (S1 Table). The resulting gap between operational costs and cumulative household WTP would then be 40.7 million KES (407,000 USD) annually, equivalent to 800 KES (8 USD) per unserved household or 4,700 KES (47 USD) per toilet (S1 Table). Estimates in the scenario of a sewer expansion to 20% of unserved households are presented in S1 Table, and result in the same annual financial gap per household or toilet.
Study summary and key findings
Rapidly growing cities in low-income countries face formidable requirements to provide improved sanitation infrastructure and services that reduce exposures to fecal waste and promote public health and economic development. Strategies to address these sanitation needs must include analyses of financing options, particularly the balance between market finance (the amount that householders pay directly or through rents), and subsidy finance (some combination of tax-based government funds, tariff-based rich to poor subsidies, and donor inputs) . Information on the amounts that householders are willing to pay directly is critical for these financing analyses. In this study, we measured the amounts that low-income households in the city of Kisumu, Kenya, were willing to pay for safely-managed latrine pit-emptying services. We also compared these amounts to the market prices of these services. We utilized two methods to determine WTP: household surveys to quantify stated WTP and randomized distribution of discount vouchers to quantify revealed WTP.
Our surveys of 942 households in low-income areas of Kisumu found that the majority (74%) relied on dry improved pit latrines, and most of the remaining households had pour-flush latrines connected to some form of underground containment (Table 2). FGD respondents noted that fecal sludge emptying was a common necessity in much of Kisumu due to high water tables, and 40% of the surveyed households reported that their underground containment was emptied in the last year (Table 2). The majority (62%) of our surveyed households utilized informal manual pit-emptiers, and most of the remainder reported emptying by a VTO (Table 2). Awareness of the formalized manual emptying businesses established through NGO efforts was low, though households responded favorably when their services were described.
In conjunction with the household surveys, we compared stated and revealed demand for two types of pit-emptying services: manual emptying by the formalized business, Gasia Poa, and vacuum truck emptying. Both stated and revealed WTP were higher for emptying by Gasia Poa (Fig 3A–3C). We surmised that this was because manual emptying was more likely to include the removal of solid waste that is commonly found in pit latrines; in post-voucher distribution follow-up surveys, respondents noted the importance of solid waste removal (Table 3). Additionally, the fact that approximately 25% of survey respondents were not accessible to VTOs likely lowered stated WTP for these services (S2 Table). Revealed WTP was lower than stated WTP for both services, though the differences were only significant for emptying by VTOs (Fig 3B and 3C). In the case of Gasia Poa, we only compared stated and revealed WTP at higher price points, which may have limited our ability to detect significant differences (Fig 3B). Nevertheless, at market prices, stated and revealed demand for both types of emptying services was low–less than 20% of households were willing to pay full market prices (Fig 3B and 3C); these results are comparable to a similar study in Rwanda that found only 15% of pits would be emptied at estimated prices that did not include subsidies .
Weak demand for safe emptying services in Kisumu was likely a combination of two factors: low income levels and the prevalence of unregulated, informal manual emptiers. Approximately half of our study population reported monthly household incomes lower than 10,000 KES (100 USD), which other studies estimated as the average income level in Kisumu LIAs [37–39]. Spread over time and amongst households sharing a toilet, safe emptying services represent a modest fraction of incomes (approximately 1%, considering annual costs of 5,000–9,500 KES per toilet shared by six households, S1 Table); despite this, a one-off payment, especially if carried by a single household as is often the case, can represent over 50–100% of a household’s monthly income and therefore compete with other priority expenditures. Additionally, informal manual emptiers are currently the most widespread form of service provision in Kisumu LIAs. Because they offer services that are 50–75% cheaper than formal service providers (Table 1), they contribute to keeping demand low. Under these circumstances, we estimated that the gap between household WTP and market prices for providing comprehensive safe emptying services to Kisumu LIAs amounted to 27.6–40.7 million KES (276,000–407,000 USD) annually (S1 Table). This gap may diminish if strict regulations are implemented to eliminate the practice of informal manual emptying.
We estimated annual emptying costs to be 50–95 USD per toilet, or 8–16 USD per household. For comparison, prior studies estimated that the annual costs of safe emptying services, in optimal scenarios with high market penetration, would amount to approximately 4–8 USD per household in Bangladesh  and 7 USD per household in Rwanda . Our cost estimates for Kisumu are slightly higher than in these other settings, though extending safe emptying services to all Kisumu households may offer opportunities for economies of scale and reduce costs. Finally, our emptying cost estimates are notably higher than the assumptions used in global cost projections: in a 2016 report estimating the costs of achieving Sustainable Development Goal 6.2 for universal sanitation, the World Bank estimated that annual OPEX would amount to 1 USD per household for a pit latrine in urban Kenya , which is approximately one order of magnitude lower than our estimates based on market prices of safe emptying services in Kisumu.
This study has several limitations. First, many households were ineligible for the study, the majority (31%) because the financial responsibility of pit emptying fell to landlords that lived offsite. It is likely that landlords living offsite may have a lower WTP for safe emptying services since they would not benefit from health, environmental, or other benefits of those services. Second, it is possible that revealed WTP may have increased if we had given households more time to redeem vouchers; though 10 households in the follow-up survey indicated that their pit was not full enough for emptying, half of these also cited other reasons, and eight met the eligibility criteria of either intending to empty their pit or having visible fecal sludge. Third, we were not able to examine revealed WTP at price points below 3000 KES (30 USD), the lowest price points for Gasia Poa. As described in the methods, we calculated the voucher price points as 20%, 40%, 60%, and 80% of the estimated price of 14,000 KES, reflecting a worst-case scenario with solid waste removal.
Safely managed onsite sanitation is gaining increasing attention as an alternative to piped sewerage in rapidly expanding cities of the developing world. FSM services, often provided by the private sector, already exist in most cities; expanding their coverage, particularly among lower income communities, is widely perceived as more cost-effective than extending and maintaining piped sewage networks and wastewater treatment plants [41–43]. Sewerage requires large capital investments and massive public infrastructure development. In contrast, scaling-up onsite sanitation is primarily seen as a market-driven activity, largely funded by customers and, in some cases, demand for recycled waste products.
Our results confirm that onsite sanitation facilities are common, particularly among the poor, in a large Kenyan city. They also show, however, that WTP in low-income neighborhoods is too low to support safe emptying services at current market prices. In theory, demand generation activities have the potential to increase WTP; however, previous research has found that sanitation demand interventions for increasing household investments in sanitation are difficult to implement successfully [44, 45]. Cost-reductions have the potential to reduce the gap between WTP and market prices, though we did not find opportunities for substantial cost-savings among pit-emptying services in Kisumu . Finally, emerging technologies may reduce the costs of safe sanitation provision: for example, the waste recovery and reuse components of CBS can offset treatment costs ; and the application of selected worm species to promote fecal sludge decomposition in pit latrines (vermifiltration) can reduce emptying requirements . Nevertheless, improving FSM in these areas will likely require large and on-going subsidies. Beyond subsidies to support operating costs, service providers will need to invest in emptying and transportation equipment to serve larger populations, and the city will need additional fecal sludge treatment capacity.
Addressing these needs for subsidies and capital investments will entail substantial coordination, planning and investment by government and donor agencies. The complexity, if not the expense, of implementation may compare to traditional sewerage development. Furthermore, it is unlikely that recently created and legally operated manual emptying businesses will compete effectively with lower-cost illegal operations. Providing safe and affordable sanitation for all residents of Kisumu, therefore, will necessitate a comprehensive sanitation market plan for the city that includes programs for subsidizing FSM for the poor, investing in transport and treatment of fecal sludge, coordination with expansion of sewerage networks, and enforcement of FSM regulations. In the absence of master plan development and execution, it is unlikely that small and fragmented FSM efforts will achieve substantial impacts, particularly among the poor.
Graphics of (a) formal manual emptying, and (b) formal manual disposal, and (c) VTOs. We used to explain these services to study participants.
S2 Fig. Example Gasia Poa voucher.
The randomized starting price points were: 3,000/6,000/8,000/11,000 KES (30/60/80/110 USD) for Gasia Poa emptying services. The full cost for Gasia Poa emptying services was 14,000 KES (140 USD).
S1 Table. Financial analysis of the capital expenditures (CAPEX) and operating expenditures (OPEX) for safe emptying in Kisumu, Kenya and comparisons with customer willingness-to-pay.
S2 Table. Bivariate subgroup analysis of stated WTP.
S3 Table. Multivariate subgroup analysis of stated WTP.
S4 Table. Bivariate and multivariate subgroup analysis of voucher redemption.
We appreciate the contributions from the Water & Sanitation for the Urban Poor (WSUP) team including Guy Norman, Sam Drabble, Rosie Renouf, and Emanuel Owako. We gratefully acknowledge our enumerators and enumerator supervisor Denish Owiti for their contributions. We also specifically thank the following Aquaya staff: Joyce Kisiangani for her contributions to enumerator training, Brian Mwangi for his contributions to enumerator training and tracking voucher redemptions, Dianne Vernon for her contributions to fieldwork management, and Sale Rhodes for her contributions to data analysis. We also thank all of the interviewees, FGD participants, and households that contributed to this study.
- 1. Cummings C, Langdown I, Hart T, Lubuva J, Kisela H. What Drives Reform? Making Sanitation a Political Priority in Secondary Cities. London, UK; 2016.
- 2. Jenkins MW, Cumming O, Cairncross S. Pit Latrine Emptying Behavior and Demand for Sanitation Services in Dar Es Salaam, Tanzania. Int J Environ Res Public Health. 2015;12:2588–611. pmid:25734790
- 3. Chowdhury S, Kone D. Business Analysis of Fecal Sludge Management: Emptying and Transportation Services in Africa and Asia. 2012.
- 4. Mansour G, Oyaya C, Owor M. Situation analysis of the urban sanitation sector in Kenya. 2017.
- 5. Burt Z, Sklar R, Murray A. Costs and Willingness to Pay for Pit Latrine Emptying Services in Kigali, Rwanda. Int J Environ Res Public Health. 2019;16(23):4738.
- 6. Balasubramanya S, Evans B, Hardy R, Ahmed R, Habib A, Asad NSM, et al. Towards Sustainable Sanitation Management: Establishing the Costs and Willingness to Pay for Emptying and Transporting Sludge in Rural Districts with High Rates of Access to Latrines. PLoS One. 2017;12(3):1–20.
- 7. Blackett I, Hawkins P. Case Studies on the Business, Policy and Technology of Faecal Sludge Management. 2nd ed. Seattle, WA: Bill & Melinda Gates Foundation; 2017.
- 8. Acey C, Kisiangani J, Ronoh P, Delaire C, Makena E, Norman G, et al. Cross-subsidies for Improved Sanitation in Low-Income Settlements: Assessing the Willingness to Pay of Water Utility Customers in Kenyan Cities. World Dev [Internet]. 2019;115:160–77. Available from: https://doi.org/10.1016/j.worlddev.2018.11.006
- 9. Norman G, Daryanani A, Peal A. Sanitation surcharges collected through water bills: A way forward for financing pro-poor sanitation. London; 2013.
- 10. Toubkiss J. Meeting the sanitation challenge in sub-Saharan cities: Lessons learnt from a financial perspective. Soc Perspect Sanit Chall. 2010;163–76.
- 11. Thye YP, Templeton M, Ali M. A Critical Review of Technologies for Pit Latrine Emptying in Developing Countries. Environ Sci Technol. 2011;41(20):1793–819.
- 12. Strande L, Ronteltap M, Brdjanovic D. Faecal Sludge Management Systems Approach for Implementation and Operation. 2014.
- 13. Tilmans S, Russel K, Sklar R, Page L, Kramer S, Davis J. Container-based sanitation: assessing costs and effectiveness of excreta management in Cap Haitien, Haiti. Environ Urban. 2015;27(1):89–104. pmid:26097288
- 14. Sanergy. Sanergy [Internet]. 2019 [cited 2019 Sep 25]. Available from: http://www.sanergy.com
- 15. Government of Kenya. Kenya Informal Settlements Improvement Project (KISIP). Nairobi, Kenya; 2014.
- 16. Melo JC. The Experience of Condominial Water and Sewerage Systems in Brazil: Case Studies from Brasilia, Salvador and Parauapebas. Washington, DC, USA; 2005.
- 17. Breidert C, Hahsler M, Reutterer T. A Review of Methods for Measuring Willingness-to-Pay. Innov Mark. 2006;2(4).
- 18. Mitchell RC, Carson RT. Using surveys to value public goods: the contingent valuation method. Resources for the Future; 1989.
- 19. Whittington D, Briscoe J, Mu X, Barron W. Estimating the Willingness to Pay for Water Services in Developing Countries: A Case Study of the Use of Contingent Valuation Surveys in Southern Haiti. Econ Dev. 1990;38(2):293–311.
- 20. County Government of Kisumu. Kisumu County Annual Development Plan (FY 2018/2019). 2018.
- 21. Furlong C, Jooust L. SFD Report Kisumu, Kenya. Kenya; 2016.
- 22. Simiyu S, Swilling M, Rheingans R, Cairncross S. Estimating the Cost and Payment for Sanitation in the Informal Settlements of Kisumu, Kenya: a Cross-sectional Study. Int J Environ Res Public Health. 2017;14(49).
- 23. Yin R. Qualitative Research from Start to Finish. Second Edi. New York: The Guilford Press; 2016.
- 24. Government of Kenya. Environmental Management and Co-ordination Act. 1999.
- 25. MajiData. MAJIDATA. 2011.
- 26. Kumpel E, Albert J, Peletz R, Waal D De, Hirn M, Uhl V, et al. Urban Water Services in Fragile States: an Analysis of Drinking Water Sources and Quality in Port Harcourt, Nigeria, and Monrovia, Liberia. Am Soc Trop Med Hyg. 2016;95(1):229–38.
- 27. Foreit J, Foreit K. The Reliability and Validity of Willingness-to-pay Surveys for Reproductive Health Pricing Decisions in Developing Countries. Health Policy (New York). 2003;63:37–47.
- 28. Altaf MA, Hughes J. Measuring the Demand for Improved Urban Sanitation Services: Results of a Contingent Valuation Study in Ouagadougou, Burkina Faso. Urban Stud. 1994;31(10):1763–76.
- 29. Gunatilake H, Yang J-C, Pattanayak S, Choe KA. Good Practices for Estimating Reliable Willingness-to-pay Values in the Water Supply and Sanitation Sector. Manila, Philippines; 2007.
- 30. Hanemann M, Loomis J, Kanninen B, Hanemann M, Loomis J, Kanninen B. Statistical Efficiency of Dichotomous Choice Contingent Valuation. Am J Agric Econ. 1991;73(4):1255–63.
- 31. Tidwell JB, Terris-prestholt F, Quaife M, Aunger R. Understanding demand for higher quality sanitation in peri-urban Lusaka, Zambia through stated and revealed preference analysis. Soc Sci Med [Internet]. 2019;232:139–47. Available from: pmid:31085398
- 32. Foster V, Araujo MC. Does infrastructure reform work for the poor? A case study from Guatemala (English) [Internet]. Policy, Re. Washington, DC, USA; 2004. Available from: http://documents.worldbank.org/curated/en/257161468749069570/Does-infrastructure-reform-work-for-the-poor-A-case-study-from-Guatemala
- 33. Arrow K, Solow R, Portney PR, Leamer EE, Radner R, Schuman H. Report of the NOAA Panel on Contingent Valuation. Fed Regist. 1993;58(10):4,601–4,614.
- 34. Chen X, Ender P, Mitchell M, Wells C. Chapter 2 –Regression Diagnostics. In: Regression with Stata [Internet]. 2003. Available from: https://stats.idre.ucla.edu/stat/stata/webbooks/reg/default.htm
- 35. KIWASCO. Key informant interview with KIWASCO on Aug 19, 2019. 2019.
- 36. Peletz R, Feng A, MacLeod C, Vernon D, Wang T, Kones J, et al. Expanding safe fecal sludge management in Kisumu, Kenya: a comparison of incentivized latrine pit emptying service model interventions. Manuscr Submitt to J Water, Sanit Hyg Dev.
- 37. Simiyu S, Cairncross S, Swilling M. Understanding Living Conditions and Deprivation in Informal Settlements of Kisumu, Kenya. Urban Forum. 2019;30:223–241.
- 38. USAID, Concern Worldwide. Indicator Development for Surveillance of Urban Emergencies (IDSUE) Year 3 Research Report. Washington, DC, USA; 2013.
- 39. USAID, Concern Worldwide. Indicator Development for Surveillance of Urban Emergencies (IDSUE) Year Four Annual Report. Washington, DC, USA; 2014.
- 40. Hutton G, Varughese M. The Costs of Meeting the 2030 Sustainable Development Goal Targets on Drinking Water, Sanitation, and Hygiene. 2016.
- 41. J-PAL. Improving Access to Urban Services for the Poor: Open Issues and a Framework for a Future Research Agenda. Cambridge, MA; 2012.
- 42. WSUP. Comparing the costs of different urban sanitation solutions in developing cities in Africa and Asia. 2018.
- 43. Daudey L. The cost of urban sanitation solutions: a literature review. J Water, Sanit Hyg Dev. 2017.
- 44. Guiteras RP, Levinsohn J, Mobarak AM. Encouraging sanitation investment in the developing world: a cluster-randomized trial [Internet]. Sciencexpress. 2015 May [cited 2015 Oct 28]. Available from: http://www.ncbi.nlm.nih.gov/pubmed/25883316
- 45. Briceño B, Coville A, Martinez S. Promoting Handwashing and Sanitation: Evidence from a Large-Scale Randomized Trial in Rural Tanzania. Policy Research Working Paper—World Bank. Washington DC; 2015.
- 46. Sklar R, Faustin C. Pit Latrines or Container Based Toilets?: A Cost-Benefit Analysis comparing two approaches to improving sanitation access in urban areas of Haiti. Copenhagen Consensus Center; 2017.