A
Onyebuchi
Obeleagu
1
Oforgbu
Evelyn
1
Faiz
ul
Islam
1
Gopi
Singh
Dharavath
1
Anum
Pervaiz
1
Navya
Vattikonda
1
Maxwell
Ambe
Etam
1✉
Phone07886220682
Email2417225@chester.ac.uk
1
Division of Public Health, Sport and Wellbeing
University of Chester
CH1 4BU
Chester
United Kingdom
Onyebuchi Obeleagu, Oforgbu Evelyn, Faiz ul Islam, Gopi Singh Dharavath, Anum Pervaiz, Navya Vattikonda, Maxwell Ambe Etam
Division of Public Health, Sport and Wellbeing, University of Chester
Corresponding author
Maxwell Ambe Etam
Division of Public Health, Sport and Wellbeing
University of Chester
Chester CH1 4BU, United Kingdom
Email: 2417225@chester.ac.uk
Phone: 07886220682.
Abstract
Aim
Cholera remains a persistent public health threat in Sub‑Saharan Africa, disproportionately affecting underserved communities with limited access to safe water, sanitation, and hygiene (WASH). Although environmental pollution is recognised as a major driver of transmission, evidence on its specific pathways and the effectiveness of related interventions remains fragmented. This review aimed to synthesise current evidence on how environmental pollution contributes to cholera outbreaks in SSA and evaluate the effectiveness of WASH and public health interventions.
Methods
A systematic search of peer‑reviewed and grey literature published between 2015 and 2025 was conducted following PRISMA guidelines. Nineteen studies met the inclusion criteria, including cross‑sectional, case‑control, cohort, and surveillance designs from nine SSA countries. Data were analysed using thematic synthesis to identify environmental drivers, high‑risk settings, behavioural contributors, and intervention outcomes.
Results
Environmental pollution was consistently associated with increased cholera risk, particularly through contaminated water sources, inadequate sanitation, open defecation, poor drainage, ineffective waste disposal, and seasonal flooding. High‑burden settings included refugee settlements, peri‑urban informal communities, and fishing populations. Behavioural factors such as limited handwashing and consumption of unwashed food further heightened vulnerability. Intervention effectiveness varied: case‑area targeted interventions and water chlorination reduced transmission, while oral cholera vaccines provided short‑term protection but were limited by incomplete coverage and waning immunity. Integrated approaches combining vaccination, WASH improvements, surveillance, and community engagement demonstrated the most consistent impact.
Conclusion
Environmental pollution is a central driver of cholera persistence in SSA. Sustainable prevention requires integrated, context‑specific strategies that strengthen WASH systems, enhance surveillance, and address structural vulnerabilities linked to poverty, displacement, and inadequate infrastructure.
Keywords:
Cholera
Sub‑Saharan Africa
Environmental pollution
WASH
Public health interventions
Introduction
Cholera remains a major global public health threat, with Sub-Saharan Africa (SSA) bearing a disproportionate burden of recurrent outbreaks and elevated mortality rates [1]. Countries including Malawi, Nigeria, Mozambique, Zambia, and the Democratic Republic of Congo continue to report substantial cholera morbidity, particularly in communities lacking sustained access to safe drinking water and adequate sanitation services [2–4]. Malawi’s 2022 epidemic, which resulted in more than 58,000 reported cases and 1,761 deaths, illustrates the severity of the ongoing cholera crisis and the limitations of reactive outbreak control strategies in the absence of long-term infrastructure investment [5, 6]. The persistence of large-scale outbreaks despite decades of global cholera control efforts highlights entrenched structural vulnerabilities across the regions [1].
Environmental pollution plays a central role in sustaining cholera transmission in SSA. Contaminated surface and groundwater sources, inadequate waste management systems, and poorly maintained sanitation infrastructure create ecological conditions that enable the environmental persistence of Vibrio cholerae [7, 8]. A global meta-analysis found high levels of V. cholerae in environmental samples, highlighting polluted water systems as important sources of ongoing transmission [9]. Across many SSA settings, rapid urbanisation and the expansion of informal settlements have outpaced infrastructural development, resulting in overcrowded environments where drainage systems, latrines, and waste disposal facilities are insufficient or entirely absent [10]. Seasonal flooding and extreme rainfall events further worsen these conditions by damaging sanitation facilities and dispersing faecal contamination into water sources used for domestic purposes [11].
Although cholera epidemiology and WASH-related interventions have been widely documented, the varying role of environmental pollution in driving recurrent and persistent outbreaks across SSA remains under-examined. While some reviews in Sub-Saharan Africa have explored environmental factors related to cholera transmission, much of the existing literature remains fragmented, with limited integration of environmental contamination, infrastructural decay, and socio-economic vulnerability within a single analytical framework [12]. This fragmented approach constrains the development of long-term, context-appropriate prevention strategies and reinforces reliance on emergency response mechanisms [3]. An integrative understanding of how environmental pollution interacts with structural determinants, including poverty, displacement, weak governance, and fragile infrastructure is essential in addressing a root cause of cholera transmission.
Communities most affected by cholera, experience multiple overlapping vulnerabilities. Refugee settlements, peri-urban informal communities, and fishing populations frequently lack reliable access to safe water and sanitation, increasing sustained exposure to contaminated environments [4, 13]. Limited access to healthcare, delayed treatment-seeking behaviour, and inadequate outbreak preparedness further heighten mortality risks during epidemics [6, 14].
This systematic review aims to examine how environmental pollution contributes to the recurrence and persistence of cholera outbreaks across Sub-Saharan Africa and to assess how public health and WASH-related interventions operate in high-risk and underserved settings. Specifically, it addresses the question of how environmental contamination, infrastructural conditions, and socio-economic vulnerability interact to influence cholera transmission dynamics. By integrating these environmental, infrastructural, and social dimensions, this review provides a structured synthesis of the pathways linking pollution, WASH deficiencies, and cholera risk. The findings are intended to inform sustainable prevention strategies, support evidence-based investments in water and sanitation infrastructure, and guide climate-resilient public health planning, with direct relevance to progress toward Sustainable Development Goals.
Methods
The review was conducted in accordance with the Preferred Reporting Items for Systematic Reviews and Meta-Analyses (PRISMA) guidelines to ensure transparency, reproducibility, and methodological rigour [15]. The PECO framework (Population, Exposure, Comparison, Outcome) was applied to structure the review question and define eligibility criteria, particularly for observational study designs relevant to environmental and public health research [16] (Appendix, Table 1).
Table 1
Study eligibility criteria defined using the PECO framework.
| |
Inclusion
|
Exclusion
|
|
Population (P)
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Studies focused on human populations in Sub-Saharan Africa (SSA), particularly communities affected by cholera outbreaks
|
Studies conducted outside Sub-Saharan Africa (SSA),
Studies focused exclusively on animal populations or laboratory strains without human/community data
|
|
Exposure (E)
|
Studies examining environmental pollution sources linked to cholera outbreaks (e.g., contaminated water, sewage discharge, industrial pollution),
Studies describing exposure to waterborne pathogens in relation to environmental contamination
|
Studies without clear link to environmental pollution as a factor
|
|
Comparison (C)
|
Studies comparing outcomes in populations with differing pollution exposures (e.g., polluted vs. less polluted areas),
Studies assessing pre- and post-intervention conditions or temporal comparisons
|
Studies without any comparison or baseline data (unless detailed descriptive data are provided)
|
|
Outcome (O)
|
Studies reporting cholera incidence, morbidity, or mortality,
Studies describing public health interventions related to cholera control,
Studies evaluating environmental and community-level socio-economic or health impacts of outbreaks/interventions
|
Studies lacking data on cholera outcomes or interventions,
Studies focused only on laboratory or molecular analyses without epidemiological or community impact data
|
|
Study Design
|
Quantitative, Cross sectional, RCT and grey studies relevant to objectives
|
Mix-method, Qualitative studies, Opinion pieces, editorials, commentaries, non-peer-reviewed blogs, or news articles without data
|
|
Time frame
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Studies Published in the last 10 years (2015–2025)
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Studies Published in the before 2015–2025
|
|
Language
|
Only English Published studies.
|
Non- English Studies without any translation
|
|
Geographical Area
|
Studies done in Sub-Saharan Africa (SSA)
|
Studies conducted outside Sub Sahara African will be excluded in this study.
|
Literature search
A
A comprehensive literature search was conducted to identify studies examining cholera outbreaks linked to environmental pollution in Sub-Saharan Africa. Searches were performed across PubMed/MEDLINE, Scopus, Google Scholar, and African Journals Online (AJOL) (Appendix, Table 2). Medical Subject Headings (MeSH) and relevant keywords were combined using Boolean operators (AND, OR). To reduce publication bias, a targeted search of grey literature was undertaken using Google Scholar and the official websites of the World Health Organization (WHO), African Ministries of Health, and credible non-governmental organisations engaged in cholera control and WASH programmes across the region [
17,
18].
Additionally, backward citation searching was conducted by reviewing the reference lists of relevant systematic reviews identified during the screening process to ensure comprehensive coverage [19].
Inclusion criteria
Investigated cholera outbreaks or transmission dynamics in Sub-Saharan Africa.
Examined environmental pollution or related factors, including water contamination, sanitation infrastructure, waste management, or flooding.
Reported empirical findings or structured reviews relevant to environmental determinants of cholera.
Were published in peer-reviewed journals or credible grey literature sources
Studies published between 2015 and 2025.
Exclusion criteria
Focused exclusively on clinical management or vaccination without environmental or WASH-related analysis.
Conducted outside Sub-Saharan Africa.
Editorials, opinion pieces, or theoretical articles lacking empirical data or systematic methodology.
Data extraction
All records retrieved from database searches, grey literature, and manual searching were imported into Excel, and duplicate entries were removed prior to screening. Study selection followed a two-stage process consistent with PRISMA guidance, with two independent reviewers screening titles and abstracts, followed by full-text assessment of eligible articles. Disagreements at any stage were resolved through discussion, with a third reviewer consulted where consensus could not be achieved. The overall study selection and screening outcomes are summarised Fig. 1.
A
A standardized data extraction table was developed to ensure consistency and completeness. Data were extracted on author, year of publication, country, study design, population characteristics, environmental exposures, public health or WASH-related interventions, community-level socio-economic or health impacts, reported outcomes, and key findings (Appendix, Table 3).
Quality appraisal
Quality and risk of bias of included studies were assessed using tools appropriate to the study design (Appendix, Table 4). Observational studies, including cross-sectional, case-control, and cohort designs, were appraised using the National Institutes of Health (NIH) Quality Assessment Tool [20]. Each study was evaluated across key domains, including study design, exposure assessment, outcome measurement, and control of confounding, and classified as having low, moderate, or high risk of bias. Quality appraisal findings were used to inform interpretation of results but did not constitute exclusion criteria.
Table 4
Risk of Bias Assessment of Included Studies.
|
Included Studies
|
Study type
|
Quality Assessment Tool
|
Quality Rating /Overall risk of Bias
|
Notable Concerns
|
|
Semá Baltazar et al., 2024
|
Prospective observational surveillance study
|
NIH Quality Assessment Tool
|
Moderate Risk of Bias
|
No sample size justification
|
|
Berhe et al., 2024
|
Observational descriptive study
|
NIH Quality Assessment Tool
|
Some risk of bias
|
No sample size justification
|
|
Bwire et al., 2017
|
Quantitative descriptive (prospective surveillance)
|
NIH Quality Assessment Tool
|
Moderate Risk of Bias
|
No adjustment for confounding
|
|
Torrea et al., 2025
|
Cross sectional survey
|
NIH Quality Assessment Tool
|
Moderate Risk of Bias
|
Self-reported data with no observational confirmation
|
|
Okeeffe et al., 2024
|
Prospective observational cohort study
|
NIH Quality Assessment Tool
|
Low Risk of Bias
|
No Major Concern
|
|
Blanton et al., 2015
|
Cross-sectional observational study
|
|
Moderate Risk of Bias
|
No sample size justification
|
|
Pande et al., 2018
|
Case-Control Study
|
NIH Quality Assessment Tool
|
Moderate Risk of Bias
|
No sample size justification
|
|
Dongdem et al., 2025
|
Cross- Sectional
|
NIH Quality Assessment Tool
|
Moderate Risk of Bias
|
Potential confounding factors
|
|
Kwesiga et al., 2017
|
Case-Control
|
NIH Quality Assessment Tool
|
Some risk of bias
|
Sample size determination concern
|
|
Mbala-Kingebeni et al., 2021
|
Case-Control
|
NIH Quality Assessment Tool
|
Low Risk of Bias
|
No Major Concern
|
|
Monje et al., 2020
|
Case-Control
|
NIH Quality Assessment Tool
|
Moderate Risk of Bias
|
No sample size justification
|
|
Mukonka et al., 2023
|
Cross Sectional study
|
NIH Quality Assessment Tool
|
Moderate Risk of Bias
|
Potential confounding factors
|
|
Ng′ombe et al., 2022
|
Longitudinal cohort study
|
NIH Quality Assessment Tool
|
Moderate Risk of Bias
|
No adjustment for confounders
|
|
Oguttu et al., 2017
|
Unmatched case-control study
|
NIH Quality Assessment Tool
|
Moderate Risk of Bias
|
Potential confounding factors
|
|
Sokemawu Freeman et al., 2024
|
Cross Sectional study
|
NIH Quality Assessment Tool
|
Moderate Risk of Bias
|
No sample size justification
|
|
Elimian et al., 2020
|
Cross Sectional study
|
NIH Quality Assessment Tool
|
Moderate Risk of Bias
|
No sample size justification
|
|
Endrise et al., 2019
|
Unmatched case-control study
|
NIH Quality Assessment Tool
|
Low Risk of Bias
|
No Major Concern
|
|
Matapo et al., 2016
|
Case-control study
|
NIH Quality Assessment Tool
|
Moderate Risk of Bias
|
Potential confounding factors
|
|
Sinyange et al., 2024
|
Cross-sectional study
|
NIH Quality Assessment Tool
|
Moderate Risk of Bias
|
Potential confounding factors
|
Data analysis and synthesis
Given the heterogeneity of study designs, environmental exposures, and outcome measures, a narrative synthesis supported by thematic analysis was undertaken. This approach enabled systematic comparison across studies, identification of recurring patterns, and exploration of relationships between environmental pollution, WASH conditions, structural vulnerability, and cholera transmission. Qualitative studies underwent thematic synthesis to identify recurring patterns and conceptual groupings. Quantitative data were summarized descriptively to highlight measurable outcomes and trends. Mixed-method studies were analyzed using integrated interpretation, aligning narrative, and statistical findings to generate cohesive insights.
This review relied on published literature and did not involve human participants. Ethical approval was not required. Ethical standards were maintained through transparent reporting, accurate citation, and responsible use of evidence.
Result
Nineteen studies published between 2015 and 2025 were included, representing several Sub-Saharan African countries: Uganda (n = 5), Zambia (n = 4), Ethiopia (n = 2), Mozambique (n = 2), Nigeria (n = 2) (Table 3). The included studies employed quantitative methodologies, including cross-sectional surveys, cohort studies, and outbreak surveillance designs. Sample sizes ranged from fewer than 100 confirmed cholera cases to studies involving more than 44,000 households.
Most studies were conducted in urban or peri-urban, low-income settings with limited access to safe water and sanitation. Extracted data were synthesized to assess links between environmental pollution and cholera outbreaks, and to evaluate the public health and socio‑economic impacts of relevant interventions.
Environmental Pollution and Cholera Risk
An association between environmental pollution and increased cholera risk was reported across reviewed studies. Studies from Mozambique linked rainfall patterns to cholera outbreaks, as floods displaced latrine waste and contaminated shared water sources [21, 22]. In Ethiopia, Berhe et al. reported that over half of affected individuals lacked latrines, while two-thirds relied on contaminated water sources [23]. Similarly, Dongdem et al. documented faecal coliform levels exceeding WHO safety limits in Ghana [24]. Evidence from Kenya showed reductions in E. coli contamination following household‑level chlorination interventions [25].
Sanitation Infrastructure and Practices
Deficient sanitation, characterized by open defecation, insufficient sewage systems, and the absence or failure of latrines, was consistently reported as a contributing factor to cholera transmission. Studies conducted in Malawi and Nigeria highlighted low latrine coverage and instances where sanitation facilities became unusable during flooding events, resulting in increased environmental contamination and exposure to faecal matter [14, 26].
Findings from Berhe et al. [23] and O’Keefe et al. [26] indicated that up to 55% of individuals in affected communities lacked access to basic sanitation services. These conditions were more pronounced in informal settlements, where unregulated waste disposal and inadequate drainage systems were commonly reported.
Hygiene Practices and Behaviors
Inadequate hygiene behaviors were frequently reported as contributors to cholera vulnerability across multiple studies [13, 27, 28]. Reported practices included limited handwashing, consumption of unwashed fruits, consumption of food from roadside vendors, and inconsistent adherence to recommended hygiene measures. One study reported a statistically significant association between failure to wash fruits before consumption and increased cholera incidence [29].
Studies also reported relatively high awareness of cholera transmission routes, alongside persistent behavioral gaps, particularly among young adults and residents of densely populated urban areas [30].
Public Health Interventions
A range of public health interventions were reported across the included studies, with water, sanitation, and hygiene (WASH) strategies commonly described. In Nigeria, O’Keefe et al. examined a case-area targeted intervention (CATI) that included soap distribution, water treatment tablets, household disinfection, and health education [26]. In Uganda, Bwire et al. reported elevated cholera case fatality rates among fishing communities characterized by limited latrine access and reliance on untreated lake water, contextual factors that informed intervention targeting [29].
Oral cholera vaccine (OCV) strategies were also evaluated. In Mozambique, Baltazar et al. reported the absence of cholera cases during OCV implementation despite persistent sanitation challenges [21]. In Zambia, Mukonka et al. documented high first-dose OCV uptake (81.3%) alongside a second-dose dropout rate of 18.8% [27].
Combined intervention approaches incorporating OCV deployment, water treatment, sanitation improvements, surveillance activities, and community engagement were reported, while single-component interventions were more commonly described in isolation [21, 26, 31]. Structural vulnerabilities, including poverty, displacement, and environmental shocks, were reported as influencing both intervention implementation and outbreak severity across settings.
Socio-Economic and Community-Level Impacts
Cholera disproportionately affected communities characterized by low income, high population density, and increased exposure to environmental hazards. In Mozambique, Torrea et al. reported that following severe flooding, 88% of households lacked basic sanitation facilities and 26% practiced open defecation [22]. Monje et al. documented prolonged outbreaks in refugee camps associated with overcrowding, reliance on stream water, and persistent hygiene challenges [13]. Similarly, in Nigeria, Elimian et al. reported that delayed access to healthcare and inadequate sanitation infrastructure in peri‑urban areas were associated with higher cholera mortality [14].
Discussion
This review examined how environmental pollution contributes to the recurrence and persistence of cholera outbreaks in Sub-Saharan Africa and how public health and WASH-related interventions perform in high-risk settings. The findings indicate that environmental pollution, particularly contamination of water sources, inadequate sanitation, and ineffective waste management, is a consistent and central factor shaping cholera transmission across diverse SSA contexts. These environmental risks are frequently intensified by flooding, poor drainage, and rapid, unplanned urbanization, reinforcing conditions that support sustained transmission rather than isolated outbreaks.
Across multiple countries, cholera incidence was repeatedly linked to faecal contamination of surface and groundwater, often following sanitation system failure during rainfall or flooding events [21, 23, 25]. The evidence suggests that pollution operates not merely as an episodic trigger but as a structural driver of cholera vulnerability, particularly where sanitation infrastructure is inadequate or poorly maintained. Importantly, nominal sanitation coverage often masked functional deficits. Studies from Uganda and Zambia demonstrated that unimproved or damaged latrine facilities, unregulated waste disposal, and ineffective drainage systems sustained environmental contamination even in communities reporting relatively high latrine access [31, 32].
Behavioral risk factors further shaped cholera transmission but were closely linked to environmental and infrastructural constraints. Poor hand hygiene, consumption of unwashed foods, and reliance on unsafe water sources were commonly reported across studies [28, 29]. However, these behaviors frequently reflected limited access to clean water, sanitation facilities, and safe food environments rather than lack of awareness. Evidence from Zambia and other settings showed that knowledge of cholera prevention did not consistently translate into safer practices where structural barriers persisted [30], highlighting the limitations of behavior-focused interventions implemented in isolation.
The review demonstrates that cholera disproportionately affects populations experiencing overlapping vulnerabilities, including poverty, displacement, and weak access to healthcare. Refugee settlements, peri-urban informal communities, and flood-affected populations consistently experienced higher outbreaks of intensity and mortality [13, 14, 22]. These findings indicate that environmental pollution interacts with socio-economic and health system constraints, compounding cholera risk and limiting the effectiveness of standard response measures.
Evaluation of interventions revealed variable effectiveness depending on context and integration. Emergency WASH measures and case-area targeted interventions reduced transmission during outbreaks, even in the absence of vaccination [26]. Oral cholera vaccines contributed to short-term control but were frequently constrained by access barriers, dose dropout, and limited duration of protection [21]. Across studies, interventions addressing a single component vaccination or hygiene promotion alone were insufficient where environmental contamination persisted.
Collectively, these findings indicate that sustained cholera control in Sub-Saharan Africa is more likely where integrated strategies address environmental pollution as a key determinant of transmission. Approaches combining vaccination, water treatment, sanitation infrastructure, surveillance, and community engagement were more consistently associated with improved outbreak control than isolated interventions. This evidence reinforces the Global Task Force on Cholera Control roadmap, emphasising multisectoral and environmentally grounded approaches aligned with long-term resilience rather than repeated emergency response.
Context‑sensitive interventions tailored to local ecological, social, and infrastructural conditions have the potential to reduce cholera risk. Recurrent outbreaks in communities exposed to unsafe water highlight the limits of vaccine‑only approaches and the need for durable structural improvements. Without addressing contaminated water sources, inadequate drainage, and poor sanitation, transmission persists despite emergency responses. Long‑term investment in essential infrastructure, alongside integration with urban planning, environmental health, and climate adaptation efforts, remains critical as climate‑related hazards such as flooding heighten vulnerability.
These findings should be interpreted considering contextual limitations. Some studies were observational, restricting causal inference. Heterogeneity in study design, outcome measures, and intervention definitions limited comparability across settings. Recall bias may have affected case–control studies, and disruptions related to conflict, displacement, and extreme weather events may have influenced data quality. Nonetheless, the consistency of patterns across countries and study designs strengthens confidence in the review that environmental contamination and inadequate WASH infrastructure remain central drivers of persistent cholera transmission in Sub‑Saharan Africa.
Conclusion
This review highlights the central role of environmental pollution in sustaining cholera transmission across Sub‑Saharan Africa, where inadequate sanitation, unsafe water, poor hygiene, and socio‑economic vulnerability remain persistent risk factors. Although vaccines and rapid response measures offer short‑term relief, long‑term control depends on addressing structural WASH deficiencies. The evidence supports integrated strategies that combine vaccination, sanitation improvements, household water treatment, behaviour change, and surveillance. To reduce recurrent outbreaks, policymakers must move beyond reactive interventions and prioritise sustained investment in drainage, waste management, and reliable water supplies, embedding cholera prevention within broader health, climate, and urban planning frameworks to strengthen long‑term resilience.
A
Clinical trial number: not applicable
A
Authors' contributions
All authors contributed to the conception, design, and development of the review. Onyebuchi Obeleagu, Oforgbu Evelyn, Faiz ul Islam, Gopi Singh Dharavath, Anum Pervaiz, and Navya Vattikonda led data collection, analysis, and initial drafting. Maxwell Ambe Etam provided intellectual refinement, strengthened the articulation of the research gap, and contributed to critical revision and final manuscript development. All authors reviewed and approved the final version.
Acknowledgements
The authors acknowledge the Torchpath research and experience program for providing an intellectual environment that supported critical discussion and independent scholarly work during the development of this manuscript.
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