Abstract Disinfection with bleach is recommended for surface cleaning in healthcare facilities, but bleach degrades over time, reducing disinfection effectiveness. We evaluated whether local bleach produced by hospitals using novel technology had adequate shelf life to justify use. Two hospitals (A and B) each produced and stored 0.5% bleach in two 20-liter plastic containers; bleach in one container was alkalinized for increased stability to pH 12; bleach in the other container was not stabilized and, for comparison, a third container of commercial bleach was tested. We tested three bleach samples from each of the containers produced by hospitals A and B, and commercial bleach for free available chlorine (FAC) using N,N-diethyl-p-phenylenediamine at irregular intervals up to 216 days. We compared the expected percent decrease in FAC per 7 days by bleach type using log-normal regression. Stabilized bleach decreased by 1% and 2% in hospitals A and B, respectively, every 7 days while non-stabilized bleach decreased by 21% and 12%, respectively (all p<0.001); commercial bleach decreased by <1% per 7 days. Bleach production proved feasible in hospitals, and both stabilized and commercial bleach maintained adequate concentration for disinfection; non-stabilized bleach maintains a useful concentration for not longer than three weeks after production.

Workers in artisanal and small-scale gold mining (ASGM) are exposed to metals and metalloids (referred to here as “metals”) while mixing milled ore and elemental mercury to produce a gold-mercury amalgam. Although concentrations of metals in surface waters near ASGM activities have been described, little is known about concentrations of metals in the water-ore-mercury slurry with which workers have extensive dermal contact. We sought to characterize those concentrations. Water samples (n = 76) were collected from amalgamation basins and milled ore washing ponds at 13 ASGM sites in Western Kenya. Samples were filtered and metals in the filtrate and metals retained on filters were analyzed for trace elements by inductively coupled plasma mass spectrometry (ICP-MS). Based upon the volume filtered and ICP-MS results, total metal concentrations in the original samples (pre-filtration), were calculated. Concentrations of metals in the amalgamation basins were high. The median concentrations of arsenic (240.23 µg/L), chromium (312.97 µg/L) and total mercury (3.52 µg/L) all exceeded Kenya’s drinking water standard by several fold. Only 3.38

While wastewater-based surveillance (WBS) has proven to be effective as an early warning system for SARS-CoV-2 monitoring in high-income countries (HICs), its feasibility in low- and middle-income countries (LMICs) is challenging due to limited sewer infrastructure, particularly outside major cities. This study evaluated SARS-CoV-2 in community-based wastewater sampling locations in addition to centralized wastewater treatment plants in Kisumu, Kenya from March 29, 2022, to March 8, 2023. The results of wastewater analysis were evaluated in relation to documented COVID-19 case counts. Wastewater samples (n = 161) were collected from centralized wastewater treatment sites (n = 41) and from decentralized sites: hospitals (n = 50), public toilets in markets (n = 31), and public toilets at transportation hubs (n = 39). Twenty-three samples (14.3%) tested positive for SARS-CoV-2 RNA. Epidemiological data were obtained from official sources. The odds of detecting one or more COVID-19 cases within 4–7 days after a positive WBS sample were 9 times higher than on days with negative WBS samples. Rates of viral RNA detection were similar for centralized and decentralized sampling sites. On five of the 32 days (15.6%) on which both centralized and decentralize samples were tested, SARS CoV-2 was detected only in the samples from decentralized sites. Centralized WBS can be supplemented with public toilet monitoring to increase the sensitivity of COVID-19 surveillance in areas with limited sewer infrastructure to enhance early detection of new cases.

Innovations to improve public sanitation facilities, especially in healthcare facilities (HCFs) in low‐income countries, are limited. SaTo pans represent novel, largely untested, modifications to reduce odour and flies and improve acceptability of HCF sanitation facilities. We conducted a pilot project to evaluate acceptability, cleanliness, flies and odour within latrines in 37 HCFs in Kisumu, Kenya, randomised into intervention (SaTo pan modifications) and control arms by sub‐county and HCF level.

Financially sustainable strategies are needed to increase access to safe drinking water in low-income settings. We designed a novel in-line chlorine doser that employs the Venturi principle to automatically add liquid chlorine at the point of water collection (tap outflows). The Venturi does not require electricity or moving parts, and users do not have to change the way they typically collect water. We field-tested the Venturi and assessed its technical performance and sales viability at water kiosks in Kisumu County, Kenya. We offered kiosk owners 6-month service packages to lease or lease-to-own the device; 27% of kiosks given a sales pitch committed to a service package. All but one kiosk paid in full during the 6-month service period and more than two-thirds purchased the device with payments totaling >$250 USD per kiosk. Kiosk customers could choose to purchase chlorinated or unchlorinated water from separate taps; 66% reported buying chlorinated water. Kiosk taps fitted with the Venturi had detectable free chlorine residual 97.6% of the time. The technical performance of the Venturi and effective demand from kiosks indicate high potential for the Venturi to increase safe water access in low-income communities.

We evaluated whether antenatal supply-side and demand-side interventions in 10 public health care facilities (HCFs) increased the percentage of women who had four or more antenatal care (ANC4+) visits and HCF deliveries from baseline to follow-up compared with women in 10 public control HCFs in Kenya. We compared maternal registry data during baseline and follow-up periods between public intervention and public control HCFs; we added seven private intervention HCFs and five private control HCFs to evaluate an unanticipated pilot insurance program that enabled women to use private intervention HCFs. From baseline to follow-up, ANC4+ visits and HCF deliveries in public intervention HCFs were 1.64 and 1.19 times greater, respectively, than in public control HCFs. Health care facility deliveries were 1.5 times higher in private intervention HCFs than public intervention HCFs. Results suggested that the combined antenatal and insurance interventions motivated increased ANC4+ visits and HCF deliveries. Women appeared to prefer private HCFs for delivery.

Despite multiple studies demonstrating the effectiveness of household water treatment with chlorine in disinfecting water and preventing diarrhea, social marketing of this intervention in low- and middle-income countries has resulted in only modest uptake. In a cluster randomized trial in Vihiga district, western Kenya, we compared uptake of household water treatment with chlorine among six villages served by community vendors trained in standard social marketing plus education through listening (ETL), an innovative behavior change method, and six villages served by community vendors trained in standard social marketing only. Water treatment uptake, water quality, and childhood diarrhea were measured over 6 months and compared between the two groups of villages. During the 6-month period, we found no association between ETL exposure and reported and confirmed household water treatment with chlorine. In both groups (ETL and comparison), reported use of water treatment was low and did not change during our 6-month follow-up. However, persons confirmed to have chlorinated water had improved bacteriologic water quality. Study findings suggest that ETL implementation was suboptimal, which, along with unexpected changes in the supply and price of chlorine, may have prevented an accurate assessment of the potential impact of ETL on water treatment behavior. Taken together, these observations exemplify the complexities of habits, practices, attitudes, and external factors that can create challenging conditions for implementing behavioral interventions. As a consequence, in this trial, ETL had no measurable impact on water treatment behavior.

Ozonation is widely used in high-income countries for water disinfection in centralized treatment facilities. New microplasma technology has reduced the energy requirements for ozone generation dramatically, such that a 15-watt solar panel is sufficient to produce small quantities of ozone. This technology has not been used previously for point-of-use drinking water treatment. We conducted a series of assessments of this technology, both in the laboratory and in homes of residents of a village in western Kenya, to estimate system efficacy and to determine if the solar-powered point-of-use water ozonation system appears safe and acceptable to end-users. In the laboratory, two hours of point-of-use ozonation reduced E. coli in 120 L of wastewater by a mean (standard deviation) of 2.3 (0.84) log-orders of magnitude and F+ coliphage by 1.54 (0.72). Based on laboratory efficacy, 10 families in Western Kenya used the system to treat 20 L of household stored water for two hours on a daily basis for eight weeks. Household stored water E. coli concentrations of >1000 most probable number (MPN)/100 mL were reduced by 1.56 (0.96) log removal value (LRV). No participants experienced symptoms of respiratory or mucous membrane irritation. Focus group research indicated that families who used the system for eight weeks had very favorable perceptions of the system, in part because it allowed them to charge mobile phones. Drinking water ozonation using microplasma technology may be a sustainable point-of-use treatment method, although system optimization and evaluations in other settings would be needed.

Background: Decentralized drinking water treatment methods generally apply membrane-based treatment approaches. Ozonation of drinking water, which previously has only been possible at large centralized facilities, can now be accomplished on a small-scale using microplasma technology. The efficacy of decentralized solar-powered drinking water treatment systems has not previously been described. Methods: We established a 1,000L decentralized solar-powered water treatment system located in Kisumu County, Kenya. Highly contaminated surface water is pumped to the treatment system, which includes flocculation and filtration steps prior to ozonation. Turbidity, total coliform bacteria, and E. coli were measured at various stages of water treatment, and bacterial log reduction values (LRVs) were calculated. Results: Forty-seven trials were conducted in which1000L of water were flocculated, filtered, and ozonated for 180 minutes. Baseline turbidity and E. coli concentrations were reduced from a median of 238 nephelometric turbidity units (NTU) and 2,419.7 most probable number/100mL, respectively, in surface water to 1.0 NTU and undetectable E. coli after ozonation for 180 minutes. The median E. coli LRV was 3.99. Conclusions: The solar-powered, decentralized water treatment system that utilizes ozonation for disinfection was founded to reduce E. coli by more than 3 log-orders of magnitude despite the high turbidity of the raw water. Further research is needed to characterize limitations, scalability, economic viability, and community perspectives that could help determine the role for similar systems in other settings.

In developing countries, most households transport water from distant sources, placing physical burdens on women and children, who commonly carry water on their heads. A lightweight backpack was developed to alleviate physical stress from water carriage and provide a safe storage container. In 2015, we conducted a baseline survey among 251 Kenyan households with children <5 years old, distributed one backpack per household, and made 6 monthly home visits to ask about backpack use. At baseline, the median reported water collection time was 40 minutes/round trip; 80% of households reported collecting water daily (median 3 times/day). At follow-up visits, respondents reported backpack use to carry water ranged from 4% to 20% in the previous day; reported backpack use for water storage in the previous day ranged from 31% to 67%. Pain from water carriage was reported at 9% of all follow-up visits. The odds of backpack use in the past day to collect water were lower during rainy season (OR: 0.3, 95% CI: 0.2–0.3) and not associated with reported pain (OR: 1.7, 95% CI: 0.9–3.3). Our study suggests that participants preferred using the backpacks for storage rather than transport of water. Further dissemination of the backpacks is not recommended because of modest use for transport.

Diarrheal illness remains a leading cause of morbidity and mortality in children < 5 years in developing countries, and contaminated water contributes to diarrhea risk. To address this problem, a novel hollow fiber ultrafilter (HFU) was developed for household water treatment. To test its impact on water quality and infant health, we conducted a cluster-randomized longitudinal evaluation in 10 intervention and 10 comparison villages in Kenya, attempting to enroll all households with infants (< 12 months old). We conducted a baseline survey, distributed HFUs to intervention households, made biweekly home visits for 1 year to assess water treatment practices and diarrhea in infants, and tested water samples from both groups every 2 months for Escherichia coli. We enrolled 92 infants from intervention households and 74 from comparison households. During the 1-year study period, 45.7% of intervention households and 97.3% of comparison households had at least one stored water sample test positive for E. coli. Compared with comparison households, the odds of E. coli contamination in stored water was lower for intervention households (odds ratio [OR]: 0.42, 95% CI: 0.24, 0.74), but there was no difference in the odds of reported diarrhea in infants, adjusting for covariates (OR: 1.19, 95% CI: 0.74, 1.90). Although nearly all water samples obtained from unprotected sources and filtered by the HFU were free of E. coli contamination, HFUs alone were not effective at reducing diarrhea in infants.

The Safe Water and AIDS Project (SWAP), a non-governmental organization in western Kenya, opened kiosks run as businesses by community health promoters (CHPs) to increase access to health products among poor rural families. We conducted a baseline survey in 2014 before kiosks opened, and a post-intervention follow-up in 2016, enrolling 1,517 households with children <18 months old. From baseline to follow-up, we observed increases in reported exposure to the SWAP program (3-11%, p = 0.01) and reported purchases of any SWAP product (3-10%, p < 0.01). The percent of households with confirmed water treatment (detectable free chlorine residual (FCR) >0.2 mg/ml) was similar from baseline to follow-up (7% vs. 8%, p = 0.57). The odds of reported diarrhea in children decreased from baseline to follow-up (odds ratios or OR: 0.77, 95% CI: 0.64-0.93) and households with detectable FCR had lower odds of diarrhea (OR: 0.53, 95% CI: 0.34-0.83). Focus group discussions with CHPs suggested that high product prices, lack of affordability, and expectations that products should be free contributed to low sales. In conclusion, modest reported increases in SWAP exposure and product sales in the target population were insufficient to impact health, but children in households confirmed to chlorinate their water had decreased diarrhea.

Efforts to provide safe water are challenged by recontamination and regrowth of pathogens in treated water during storage. This study evaluated the potential of metallic silver with a chemically etched surface to reduce recontamination risks during water storage in ceramic water filters. Batch experiments were conducted in the laboratory with water storage buckets containing three configurations of varying amounts of silver. Field trials in a rural area in Kenya assessed the effect of the same configurations in the storage buckets of locally produced ceramic pot filters without colloidal silver coating. The tests revealed that the etched silver slightly reduced microbiological recontamination risks during water storage despite the low diffusion of silver ions (<5 µg Ag/L). The effect was strongly influenced by water chemistry parameters. A statistically significant difference in the removal of E. coli (Δ Log Removal Value (LRV) = 0.6) and total coliforms (Δ LRV = 1.7) was found between households using a filter with silver in the water reservoir and those using a filter without silver. Multivariate regression of water handling factors and hygiene practices on filter performance revealed that the presence of silver in the reservoir and cleaning the filter element with a brush were associated with a better filter performance.

An antimicrobial towel designed for repeated use was developed to prevent recontamination of washed hands after drying. This field trial in Kenya found that nearly all antimicrobial hand towels and untreated control towels were contaminated with E. coli after household use. The antimicrobial towel did not inactivate E. coli.

To address water and hygiene infrastructure deficiencies in health-care facilities (HCFs) in Siaya County, Kenya, portable water stations, soap, and water treatment products were provided to 109 HCFs in 2005. In 2011 and again in 2016, we interviewed staff in 26 randomly selected HCFs, observed water sources, water stations, and tested source and stored water for chlorine residual and Escherichia coli. Of 26 HCFs, 22 (85%) had improved water supplies, and 22 (85%) had functioning handwashing and drinking water stations, but < 50% provided soap or water treatment. Thirteen (50%) of 26 source water samples yielded E. coli; 24 (92%) of 26 stored water samples yielded no E. coli, including nine with residual chlorine and nine untreated samples from sources yielding no E. coli. Eleven years after implementation, 85% of HCFs continued to use water stations that protected water from recontamination. Sustainable provision of soap and water treatment products could optimize intervention use.

Poor hand hygiene contributes to diarrhea in developing countries. Handwashing with soap reduces diarrhea risk, but drying hands on contaminated towels can compromise the benefits of handwashing. In response to the challenge of keeping hands clean, an antimicrobial hand towel was developed and shown to be promising in the laboratory, but has not been adequately tested in the field. We evaluated the effectiveness of an antimicrobial towel in two randomized, double-blinded crossover trials among mothers with children<5 years old in 125 households in western Kenya. In trial 1, we randomly assigned mothers to use either the treated towel or an identical untreated (placebo) towel and made surprise home visits at random times once a week for three weeks. At each visit, we tested hands for Escherichia coli using sterile hand rinses, then switched towel types in the two groups and repeated three weekly rounds of E. coli testing. In crossover trial 2, we compared E. coli contamination of maternal hands immediately following three different handwashing/drying procedures: soap and water + treated towel, water only + treated towel, and soap and water + air dry. There was no statistically significant difference in the level of E. coli contamination on maternal hands by type of towel used during trial 1 (odds ratio for treated vs untreated towel: 1.14, 95% confidence interval 0.83-1.56). In trial 2, there were no significant differences in E. coli contamination of maternal hands by handwashing/drying procedure. In these trials, use of antimicrobial hand towels did not prevent E. coli contamination of mothers' hands in Kenyan households during random testing and offered no advantages over standard handwashing and drying practices. Handwashing with soap and clean water and drying with clean towels are recommended. (C) 2019 Elsevier Ltd. All rights reserved.

Background: From December 2014 to September 2016, a cholera outbreak in Kenya, the largest since 2010, caused 16,840 reported cases and 256 deaths. The outbreak affected 30 of Kenya's 47 counties and occurred shortly after the decentralization of many healthcare services to the county level. This mixed-methods study, conducted June-July 2015, assessed cholera preparedness in Homa Bay, Nairobi, and Mombasa counties and explored clinic-and community-based health care workers' (HCW) experiences during outbreak response. Methods: Counties were selected based on cumulative cholera burden and geographic characteristics. We conducted 44 health facility cholera preparedness checklists (according to national guidelines) and 8 focus group discussions (FGDs). Frequencies from preparedness checklists were generated. To determine key themes from FGDs, inductive and deductive codes were applied; MAX software for qualitative data analysis (MAXQDA) was used to identify patterns. Results: Some facilities lacked key materials for treating cholera patients, diagnosing cases, and maintaining infection control. Overall, 82% (36/44) of health facilities had oral rehydration salts, 65% (28/43) had IV fluids, 27% (12/44) had rectal swabs, 11% (5/44) had Cary-Blair transport media, and 86% (38/44) had gloves. A considerable number of facilities lacked disease reporting forms (34%, 14/41) and cholera treatment guidelines (37%, 16/43). In FDGs, HCWs described confusion regarding roles and reporting during the outbreak, which highlighted issues in coordination and management structures within the health system. Similar to checklist findings, FGD participants described supply challenges affecting laboratory preparedness and infection prevention and control. Perceived successes included community engagement, health education, strong collaboration between clinic and community HCWs, and HCWs' personal passion to help others. Conclusions: The confusion over roles, reporting, and management found in this evaluation highlights a need to adapt, implement, and communicate health strategies at the county level, in order to inform and train HCWs during health system transformations. International, national, and county stakeholders could strengthen preparedness and response for cholera and other public health emergencies in Kenya, and thereby strengthen global health security, through further investment in the existing Integrated Disease Surveillance and Response structure and national cholera prevention and control plan, and the adoption of county-specific cholera control plans.

Household water treatment with chlorine can improve microbiological quality and reduce diarrhea. Chlorination is typically assessed using free chlorine residual (FCR), with a lower acceptable limit of 0.2 mg/L, however, accurate measurement of FCR is challenging with turbid water. To compare potential measures of adherence to treatment and water quality, we chlorinated recently-collected water in rural Kenyan households and measured total chlorine residual (TCR), FCR, oxidation reduction potential (ORP), and E. coli concentration over 72 h in clay and plastic containers. Results showed that 1) ORP served as a useful proxy for chlorination in plastic containers up to 24 h; 2) most stored water samples disinfected by chlorination remained significantly less contaminated than source water for up to 72 h, even in the absence of FCR; 3) TCR may be a useful proxy indicator of microbiologic water quality because it confirms previous chlorination and is associated with a lower risk of E. coli contamination compared to untreated source water; and 4) chlorination is more effective in plastic than clay containers presumably because of lower chlorine demand in plastic.

To assess the health impact of reusable, antimicrobial hand towels, we conducted a cluster randomized, yearlong field trial. At baseline, we surveyed mothers, and gave four towels plus hygiene education to intervention households and education alone to controls. At biweekly home visits, we asked about infections in children < 2 years old and tested post-handwashing hand rinse samples of 20% of mothers for Escherichia coli. At study's conclusion, we tested 50% of towels for E. coli. Baseline characteristics between 188 intervention and 181 control households were similar. Intervention and control children had similar rates of diarrhea (1.47 versus 1.48, P = 0.99), respiratory infections (1.38 versus 1.48, P = 0.92), skin infections (1.76 versus 1.79, P = 0.81), and subjective fever (2.62 versus 3.40, P = 0.04) per 100 person-visits. Post-handwashing hand contamination was similar; 67% of towels exhibited E. coli contamination. Antimicrobial hand towels became contaminated over time, did not improve hand hygiene, or prevent diarrhea, respiratory infections, or skin infections.

Although anemia in preschool children is most often attributed to iron deficiency, other nutritional, infectious, and genetic contributors are rarely concurrently measured. In a population-based, cross-sectional survey of 858 children 6–35 months of age in western Kenya, we measured hemoglobin, malaria, inflammation, sickle cell, α-thalassemia, iron deficiency, vitamin A deficiency, anthropometry, and socio-demographic characteristics. Anemia (Hb < 11 g/dL) and severe anemia (Hb < 7 g/dL) prevalence ratios (PRs) for each exposure were determined using multivariable modeling. Anemia (71.8%) and severe anemia (8.4%) were common. Characteristics most strongly associated with anemia were malaria (PR: 1.7; 95% confidence interval [CI] = 1.5–1.9), iron deficiency (1.3; 1.2–1.4), and homozygous α-thalassemia (1.3; 1.1–1.4). Characteristics associated with severe anemia were malaria (10.2; 3.5–29.3), inflammation (6.7; 2.3–19.4), and stunting (1.6; 1.0–2.4). Overall 16.8% of anemia cases were associated with malaria, 8.3% with iron deficiency, and 6.1% with inflammation. Interventions should address malaria, iron deficiency, and non-malarial infections to decrease the burden of anemia in this population.