Abstract
In household environments, the improper handling of children's feces can be a significant contaminant, raising a high risk of child exposure. Thus, the objective of this study was to pool the available evidence on the prevalence of safe child feces disposal practices and their association with reported childhood diarrhea in low-income and middle-income countries. PubMed, Science Direct, Cochrane Library databases, Ovid Medline, Google Scholar, and references of other studies were searched. The search was limited to studies published in English-language literature. Two independent reviewers used an appropriate tool to critically appraise the selected studies. Stata version 16 was used for the analysis. The pooled prevalence of unsafe disposal of children's feces among 20 studies was 52.63% (95% CI: 0.43–0.62). Overall, the meta-analysis found that unsafe disposal practices insignificantly increased the risk of diarrhea by 4% (OR: 1.04, 95% CI: 0.84–1.24). In the subgroup analysis, unsafe disposal of children's feces decreased the risk of diarrhea in Oceania (OR = 0.75, 95% CI = 0.62–0.88) and increased in Asia (OR = 1.33, 95% CI = 1.25–1.41). In conclusion, the prevalence of unsafe child feces disposal practices was high. There was no significant association between unsafe child feces disposal practices and diarrhea.
HIGHLIGHTS
This study aimed to pool the extent of disposal of children's feces and its association with diarrhea in children.
This systematic review and meta-analysis included 19 published articles and 1 unpublished study.
The pooled prevalence of unsafe maternal/guardian disposal practices for child feces in this study was high.
Unsafe disposal practices for children's feces insignificantly increased the likelihood of diarrhea in children.
BACKGROUND
Each year, 829,000 people in low- and middle-income countries die as a result of inadequate water, sanitation, and hygiene, accounting for 60% of all diarrhoeal deaths (WHO 2022). Unsafe sanitation is one of the world's most serious health and environmental problems, particularly for the poorest people. In 2017, an estimated 775,000 people died as a result of unsafe sanitation. This accounted for 1.4% of all deaths worldwide. Unsafe sanitation also accounts for 5% of deaths in low-income countries (Hannah & Roser 2021). It is estimated to cause 432,000 diarrheal deaths each year and is also a major contributor to numerous neglected tropical diseases such as intestinal worms, schistosomiasis, and trachoma, as well as contributing to malnutrition (WHO 2019).
Globally, over 1.7 billion people do not have access to basic sanitation services such as private toilets and latrines. Of these, 494 million continue to defecate in the open, such as in street gutters, behind bushes, or in open bodies of water (WHO 2022). Adopting safe child feces disposal practices necessitates the availability of improved latrines (Majorin et al. 2014; Sara & Graham 2014). A previous study, however, showed that some respondents who had a latrine practiced unsafe child feces disposal, suggesting that improvement and the provision of physical infrastructure are insufficient to ensure the adoption of appropriate hygiene practices (Sahiledengle 2020).
Fecal contamination from children aged 3 months to 5 years old in the home environment was widespread both inside and outside the home, according to studies conducted in an urban slum in Nairobi, Kenya, and rural Odisha, India (Bauza et al. 2017, 2020). According to studies, leaving child feces out in the open or failing to dispose of it is a common child feces disposal practice (Sultana et al. 2013; Majorin et al. 2014). Findings showed that the prevalence of unsafe child feces disposal varies from country to country. The highest prevalence was reported in Nigeria (80.33%) (Aluko et al. 2017), Bangladesh (80.33%) (Islam et al. 2020), and India (79.00%) (Bawankule et al. 2017). In contrast, studies from Ethiopia (9.20%) (Alemayehu et al. 2021), Kenya (30%) (World Bank/UNICEF 2015), and Cambodia (29.27%) (Vong et al. 2021) reported the lowest prevalence.
Improper disposal of children's feces can be a major contaminant in household settings and pose a high risk of exposure to infants. The study reported from Indonesia showed that households that do not dispose of children's feces safely are significantly more likely to have diarrhea than households that practice safe disposal (Cronin et al. 2016; Majorin et al. 2019). According to a meta-analysis study, unsafe child feces disposal practices like open defecation, stool disposal in the open, stools not removed from soil, and feces observed on the ground increased the risk of diarrheal diseases by 23% (Gil et al. 2004). Several studies done in Nepal (Lamichhane et al. 2018), Indonesia (Cronin et al. 2016), Thailand (Wilunda & Alessio 2009), Cambodia (Vong et al. 2021), India (Bawankule et al. 2017), and Kenya (World Bank/UNICEF 2015) have linked unsafe fecal disposal to an increased risk of childhood diarrhea. However, studies conducted in Ethiopia (Sahiledengle 2020), Papua New Guinea (Seidu et al. 2020), Nigeria (Aluko et al. 2017), and Eswatini (Simelane et al. 2020) found that unsafe fecal disposal in children reduces the risk of childhood diarrhea. It might be that the availability of physical infrastructure alone is insufficient to assure the adoption of safe child feces disposal practices.
Previously conducted studies in various low- and middle-income countries revealed that the prevalence of unsafe practices for disposing of children's feces, as well as the association of unsafe fecal disposal with diarrhea, had conflicting results, and no attempts have been made to systematically review this. Thus, the current study aimed to synthesize the available evidence on unsafe fecal disposal practices in children and its association with diarrhea in children in low- and middle-income countries based on this evidence. In this study, the research questions addressed in this review were: (1) What is the extent of unsafe practices for disposal of child feces in low- and middle-income countries? (2) Is there a link between unsafe child feces disposal practices and diarrhea in low- and middle-income countries?
METHODS AND ANALYSIS
Study design and protocol
This systematic review and meta-analysis was written following the reporting guidelines in the PRISMA guidelines (Preferred Reporting Items for Systematic Reviews and Meta-analyses) (Moher et al. 2009). The four phases drawn from the PRISMA flowchart were documented in the results to show the study selection process from the initially identified records to the eventually included studies (Moher et al. 2009). The review protocol was registered in the PROSPERO database (Registration ID: CRD42020189034).
Eligibility criteria
The systematic review and meta-analysis included published and unpublished observational studies conducted in low- and middle-income countries that examined the magnitude of unsafe child feces disposal practices and its association with reported diarrhea. Our population of interest were mothers/guardians with children under 5 years of age, regardless of gender, race, and socio-economic status. The outcome of interest was the pooled prevalence of unsafe disposal practices for children's feces and its association with reported diarrhea. The review includes only reports prepared in English, regardless of the year of publication. Previously published systematic reviews and qualitative studies were not included.
Information sources and search strategy
PubMed, Science Direct, Cochrane Library databases, and Ovid Medline electronic resources were used to find relevant literature for this review. In addition, we searched Google Scholar and references from other studies. The literature search was carried out by the first author in July 2021. The search strategy was limited to studies published in English literature. We used terms from Medical Subject Headings (MeSH) from PubMed and combined keywords to identify studies in the databases (‘unsafe’ and ‘child’ and ‘feces disposal’ and ‘association’ and ‘diarrhea’ and ‘low-income and middle-income countries’). A complete search strategy for PubMed is given in Supplementary Material, Table S1.
Study selection process
The search results were exported to Mendeley Desktop reference management software, version 1.19.5 (Mendeley Ltd, Elsevier, The Netherlands) and then duplicates were eliminated. The studies were screened by two independent review authors (NES and DBG). Articles found through database searches were evaluated for inclusion at three levels, i.e., by title, then by abstract, and finally by full text. The full texts of selected studies were retrieved and assessed in detail against the inclusion criteria. Discrepancies were discussed between the reviewers, and the inclusion criteria were refined. In the case of uncertainty in the decision to include or exclude an item, the reviewer included that item for the next level of screening. The documents without abstracts were viewed at the full-text level.
Data extraction
The JBI Adapted Data Extraction Form was used to extract the study characteristics and status of children's fecal disposal practices and the odds ratios showing the association between unsafe disposal of children's feces and reported diarrhea. A structured extraction excel sheet was created, and information from each record was collected using this excel sheet for the systematic review. For each study, the author's name and year of publication, country of origin and group of included studies, type of included study, sample size, description of child fecal disposal practices, and results of included studies were extracted by two reviewers. Any disagreements between the reviewers were resolved through discussion or with a third reviewer.
Outcome of interest
The primary outcome of this review was the pooled prevalence of unsafe disposal of children's feces, and the secondary outcome of this study was the estimate of the association between unsafe disposal of children's feces and reported diarrhea. Disposal of children's feces was defined based on the WHO/UNICEF-JMP on water supply and sanitation (WHO/UNICEF 2006) as safe disposal when households responded that they were collected and disposed of in a latrine or buried, and unsafe disposal when they said they were put down a drain or ditch, thrown in the trash, or left open. Whereas diarrhea is defined as three or more loose or watery stools in a 24-hour period, or any loose stool that contains blood or mucus.
Evaluation of study quality
The methodological quality of all studies that met the selection criteria was independently assessed by two authors (NES and DBG) using the Critical Appraisal Tools of the Joanna Briggs Institute (JBI) (Aromataris & Munn 2020). Each study was individually and independently assessed by the two reviewers, both at the outcome and study level, to generate an overall risk of bias score. The two authors' scores for each bias criterion were then compared. Disagreements between the two authors regarding individual bias criteria were identified and discussed to reach consensus. Studies with a score of ≥7 were considered high quality, studies with a score of 4–6 were considered moderate quality, and studies with a score of ≤3 were considered low quality.
Data synthesis and statistical analysis
The individual studies were concisely described using an overview table. The summary table describes in particular the characteristics of the included studies and the most important results. Based on the summary table, we first performed a narrative synthesis to describe the characteristics of the included studies and the main findings. Then, using Stata Version 16 (College Station, TX 77845, USA), a random effects model was used to perform a meta-analysis. If the included study did not provide a 95% confidence interval (CI) for the prevalence of child feces disposal practices, the 95% CI was derived using the standard error (SE) and prevalence of child feces disposal practices from each included study. SE was calculated using the formula for studies that did not present it. The calculated SE and prevalence of each study were then entered into Stata software to calculate the overall pooled prevalence of unsafe child feces disposal practices and its 95% CI. Similarly, the association between unsafe child feces disposal practices and reported diarrhea was summarized using statistical estimates of effect size, odds ratio (OR), and 95% CI of the study factors. Subgroup analyses were conducted depending on the study region/continent and data source (demographic and health surveys (DHS) or not). After excluding one study (leave-one-out), a sensitivity analysis was performed to determine the impact of each study on the pooled estimate.
Heterogeneity was assessed statistically using a chi-square test (Q-test) for statistics and an inverse variance index (I2) (Higgins & Thompson 2002). The I2 values were classified as follows: no relevant heterogeneity (0–25%), moderate heterogeneity (25–50%), and significant heterogeneity (50–100%). The data were considered homogeneous when I2 was ≤50%. Fixed effects models were used to construct summary ORs and 95% CIs where there was no heterogeneity. Where there was statistical heterogeneity, random effects models were applied. Forest plots were created to show the pooled estimates with a 95% CI. In a forest plot, the box in the middle of each horizontal line (confidence interval, CI) represents the point estimate of the effect for a single study. The box's size reflects how much the study weighs in comparison to the combined estimate. The diamond represents the overall effect estimate of the meta-analysis. The pooled effect point estimate is represented by the diamond's center on the x-axis, and the 95% CI around that point estimate is shown by the diamond's width (Chang et al. 2022). A funnel plot and the Eggers test for publication bias were used to assess publication bias. The symmetrical funnel plot and the insignificant Eggers test were used to argue no serious publication.
RESULTS
Study selection process
Flowchart of study selection for systematic review and meta-analysis of unsafe child feces disposal practices and its association with childhood diarrhea.
Flowchart of study selection for systematic review and meta-analysis of unsafe child feces disposal practices and its association with childhood diarrhea.
Characteristics of the included studies
In a total of 865 published and unpublished records, 20 cross-sectional studies that met the inclusion criteria and focused on the prevalence of unsafe fecal disposal practices in children and their association with childhood diarrhea were included in the analysis. The current meta-analysis included eight studies from Ethiopia (Mihrete et al. 2014; Azage & Haile 2015; Sahiledengle 2019, 2020; Alemayehu et al. 2021; Getahun & Adane 2021; Soboksa 2021; Soboksa et al. 2021), two studies from Nigeria (Aluko et al. 2017; Aliyu & Dahiru 2019), two studies from Indonesia (Cronin et al. 2016; Sidabalok et al. 2019), one each from India (Bawankule et al. 2017), Papua New Guinea (Seidu et al. 2020), Eswatini (Simelane et al. 2020), Cambodia (Vong et al. 2021), Thailand (Wilunda & Alessio 2009), Bangladesh (Islam et al. 2020), Kenya (Siruri 2013), and a study that compiled DHS from 15 sub-Saharan African countries (Seidu et al. 2021) were represented. The sample size of the study ranged from 221 to 128,096 participants. The prevalence of unsafe disposal of child feces ranged from 9.20 to 80.33%. The lowest prevalence of unsafe disposal of children's feces was reported in a study conducted by Alemayehu et al. (2021) in Ethiopia (Alemayehu et al. 2021), whereas the highest prevalence of unsafe disposal of child feces was reported in a study conducted in Nigeria by Aluko et al. (2017) (Table 1).
Descriptive summary of 20 studies included in the systematic review and meta-analysis
S.No . | Author, publication year . | Study site . | Study design . | Sample size . | Age group included . | Prevalence of unsafe disposal (%) with 95% CI . |
---|---|---|---|---|---|---|
1. | Aliyu & Dahiru (2019) | Nigeria | Cross-sectional | 19,288 | <5 | 40.60 (39.91–41.30) |
2. | Azage & Haile (2015) | Ethiopia | Cross-sectional | 11,126 | <5 | 66.32 (65.44–67.20) |
3. | Bawankule et al. (2017) | India | Cross-sectional | 35,273 | <5 | 79.00 (78.57–79.42) |
4. | Cronin et al. (2016) | Indonesia | Cross-sectional | 4,909 | <2 | 52.80 (51.39–54.21) |
5. | Sahiledengle (2020) | Ethiopia | Cross-sectional | 20,629 | <5 | 77.70 (76.30–79.00) |
6. | Sahiledengle (2019) | Ethiopia | Cross-sectional | 4,145 | <5 | 63.10 (59.50–66.60) |
7. | Seidu et al. (2020) | Papua New Guinea | Cross-sectional | 2,095 | <5 | 56.00 (54.50–58.00) |
8. | Seidu et al. (2021) | 15 Sub-Sahara Africa countries | Cross-sectional | 128,096 | <5 | 41.27 (41.00–41.54) |
9. | Simelane et al. (2020) | Eswatini | Cross-sectional | 2,765 | <3 | 41.80 (39.30–44.40) |
10. | Vong et al. (2021) | Cambodia | Cross-sectional | 5,745 | <5 | 29.27 (27.51–31.09) |
11. | Mihrete et al. (2014) | Ethiopia | Cross-sectional | 925 | <5 | 55.40 (51.86–58.37) |
12. | Sidabalok et al. (2019) | Indonesia | Cross-sectional | 1,007 | <5 | 42.70 (39.62–45.82) |
13. | Alemayehu et al. (2021) | Ethiopia | Cross-sectional | 620 | <5 | 9.20 (7.04–11.75) |
14. | Wilunda & Alessio (2009) | Thailand | Cross-sectional | 5,658 | <5 | 35.35 (34.10–36.61) |
15. | Soboksa (2021) | Ethiopia | Cross-sectional | 9,754 | <5 | 75.20 (74.30–76.02) |
16. | Islam et al. (2018) | Bangladesh | Cross-sectional | 803 | <5 | 80.00 (76.75–82.43) |
17. | Getahun & Adane (2021) | Ethiopia | Cross-sectional | 485 | <5 | 43.20 (38.84–47.84) |
18. | Aluko et al. (2017) | Nigeria | Cross-sectional | 300 | <5 | 80.33 (75.38–84.68) |
19. | Soboksa et al. (2021) | Ethiopia | Cross-sectional | 756 | <5 | 69.58 (66.16–72.89) |
20. | Siruri (2013) | Kenya | Cross-sectional | 221 | <5 | 13.57 (9.35–18,81) |
S.No . | Author, publication year . | Study site . | Study design . | Sample size . | Age group included . | Prevalence of unsafe disposal (%) with 95% CI . |
---|---|---|---|---|---|---|
1. | Aliyu & Dahiru (2019) | Nigeria | Cross-sectional | 19,288 | <5 | 40.60 (39.91–41.30) |
2. | Azage & Haile (2015) | Ethiopia | Cross-sectional | 11,126 | <5 | 66.32 (65.44–67.20) |
3. | Bawankule et al. (2017) | India | Cross-sectional | 35,273 | <5 | 79.00 (78.57–79.42) |
4. | Cronin et al. (2016) | Indonesia | Cross-sectional | 4,909 | <2 | 52.80 (51.39–54.21) |
5. | Sahiledengle (2020) | Ethiopia | Cross-sectional | 20,629 | <5 | 77.70 (76.30–79.00) |
6. | Sahiledengle (2019) | Ethiopia | Cross-sectional | 4,145 | <5 | 63.10 (59.50–66.60) |
7. | Seidu et al. (2020) | Papua New Guinea | Cross-sectional | 2,095 | <5 | 56.00 (54.50–58.00) |
8. | Seidu et al. (2021) | 15 Sub-Sahara Africa countries | Cross-sectional | 128,096 | <5 | 41.27 (41.00–41.54) |
9. | Simelane et al. (2020) | Eswatini | Cross-sectional | 2,765 | <3 | 41.80 (39.30–44.40) |
10. | Vong et al. (2021) | Cambodia | Cross-sectional | 5,745 | <5 | 29.27 (27.51–31.09) |
11. | Mihrete et al. (2014) | Ethiopia | Cross-sectional | 925 | <5 | 55.40 (51.86–58.37) |
12. | Sidabalok et al. (2019) | Indonesia | Cross-sectional | 1,007 | <5 | 42.70 (39.62–45.82) |
13. | Alemayehu et al. (2021) | Ethiopia | Cross-sectional | 620 | <5 | 9.20 (7.04–11.75) |
14. | Wilunda & Alessio (2009) | Thailand | Cross-sectional | 5,658 | <5 | 35.35 (34.10–36.61) |
15. | Soboksa (2021) | Ethiopia | Cross-sectional | 9,754 | <5 | 75.20 (74.30–76.02) |
16. | Islam et al. (2018) | Bangladesh | Cross-sectional | 803 | <5 | 80.00 (76.75–82.43) |
17. | Getahun & Adane (2021) | Ethiopia | Cross-sectional | 485 | <5 | 43.20 (38.84–47.84) |
18. | Aluko et al. (2017) | Nigeria | Cross-sectional | 300 | <5 | 80.33 (75.38–84.68) |
19. | Soboksa et al. (2021) | Ethiopia | Cross-sectional | 756 | <5 | 69.58 (66.16–72.89) |
20. | Siruri (2013) | Kenya | Cross-sectional | 221 | <5 | 13.57 (9.35–18,81) |
Risk of bias
The quality of the included studies was assessed using the JBI checklist for analytical cross-sectional studies (Moola et al. 2020). Among the 20 included studies, 14 of the included studies were high-quality studies (Azage & Haile 2015; Cronin et al. 2016; Bawankule et al. 2017; Islam et al. 2018; Aliyu & Dahiru 2019; Sahiledengle 2019, 2020; Seidu et al. 2020, 2021; Simelane et al. 2020; Getahun & Adane 2021; Soboksa 2021; Soboksa et al. 2021; Vong et al. 2021), while 6 studies were of moderate (Wilunda & Alessio 2009; Siruri 2013; Mihrete et al. 2014; Aluko et al. 2017; Sidabalok et al. 2019; Alemayehu et al. 2021) according to our assessment (Supplementary Material, Table S2).
Prevalence of unsafe child feces disposal
Forest plot of the pooled prevalence of unsafe child feces disposal practices of 20 studies included in the systematic review and meta-analysis.
Forest plot of the pooled prevalence of unsafe child feces disposal practices of 20 studies included in the systematic review and meta-analysis.
Association between unsafe disposal practice child feces and diarrhea
Forest plot of the pooled odds ratio of unsafe child feces disposal practices and childhood diarrhea.
Forest plot of the pooled odds ratio of unsafe child feces disposal practices and childhood diarrhea.
Subgroup analysis
Forest plot of the subgroup analysis by region pooled odds ratio of unsafe child feces disposal practices and childhood diarrhea.
Forest plot of the subgroup analysis by region pooled odds ratio of unsafe child feces disposal practices and childhood diarrhea.
Forest plot of the subgroup analysis by data source pooled odds ratio of unsafe child feces disposal practices and childhood diarrhea.
Forest plot of the subgroup analysis by data source pooled odds ratio of unsafe child feces disposal practices and childhood diarrhea.
Sensitivity analysis
The sensitivity analysis of the relationship between unsafe methods of disposing of children's feces and diarrhea in children is presented in Table 2. To identify the potential source of heterogeneity in the analysis, a leave-one-out sensitivity analysis related to unsafe methods of disposing of childhood feces and childhood diarrhea was performed. According to the results, not a single study had an effect on overall childhood diarrhea.
Sensitivity analysis of 20 studies included in the systematic review and meta-analysis of unsafe child feces disposal practices and its association with childhood diarrhea
No. . | Omitted study . | Pooled odds ratio . | (95% CI) . | I2 . | P-value . |
---|---|---|---|---|---|
1 | Aliyu & Dahiru (2019) | 1.05 | 0.84–1.26 | 97.67 | 0.001 |
2 | Azage & Haile (2015) | 1.05 | 0.84–1.27 | 97.49 | 0.001 |
3 | Bawankule et al. (2017) | 1.02 | 0.81–1.24 | 97.27 | 0.001 |
4 | Cronin et al. (2016) | 1.02 | 0.81–1.22 | 97.43 | 0.001 |
5 | Sahiledengle (2020) | 1.06 | 0.84–1.29 | 97.68 | 0.001 |
6 | Sahiledengle (2019) | 1.07 | 0.86–1.29 | 97.57 | 0.001 |
7 | Seidu et al. (2020) | 1.06 | 0.85–1.28 | 97.75 | 0.001 |
8 | Seidu et al. (2021) | 1.07 | 0.84–1.29 | 97.22 | 0.001 |
9 | Simelane et al. (2020) | 1.07 | 0.84–1.29 | 97.84 | 0.001 |
10 | Vong et al. (2021) | 1.02 | 0.80–1.23 | 97.58 | 0.001 |
11 | Mihrete et al. (2014) | 1.08 | 0.88–1.28 | 97.23 | 0.001 |
12 | Sidabalok et al. (2019) | 1.00 | 0.81–1.20 | 97.23 | 0.001 |
13 | Alemayehu et al. (2021) | 1.01 | 0.82–1.21 | 97.35 | 0.001 |
14 | Wilunda & Alessio (2009) | 1.02 | 0.81–1.23 | 97.48 | 0.001 |
15 | Soboksa (2021) | 1.07 | 0.85–1.29 | 97.66 | 0.001 |
16 | Islam et al. (2018) | 1.04 | 0.83–1.25 | 97.63 | 0.001 |
17 | Getahun & Adane (2021) | 1.01 | 0.81–1.20 | 97.25 | 0.001 |
18 | Aluko et al. (2017) | 1.07 | 0.89–1.29 | 96.69 | 0.001 |
19 | Soboksa et al. (2021) | 1.00 | 0.80–1.20 | 97.41 | 0.001 |
20 | Siruri (2013) | 1.03 | 0.83–1.23 | 97.52 | 0.001 |
No. . | Omitted study . | Pooled odds ratio . | (95% CI) . | I2 . | P-value . |
---|---|---|---|---|---|
1 | Aliyu & Dahiru (2019) | 1.05 | 0.84–1.26 | 97.67 | 0.001 |
2 | Azage & Haile (2015) | 1.05 | 0.84–1.27 | 97.49 | 0.001 |
3 | Bawankule et al. (2017) | 1.02 | 0.81–1.24 | 97.27 | 0.001 |
4 | Cronin et al. (2016) | 1.02 | 0.81–1.22 | 97.43 | 0.001 |
5 | Sahiledengle (2020) | 1.06 | 0.84–1.29 | 97.68 | 0.001 |
6 | Sahiledengle (2019) | 1.07 | 0.86–1.29 | 97.57 | 0.001 |
7 | Seidu et al. (2020) | 1.06 | 0.85–1.28 | 97.75 | 0.001 |
8 | Seidu et al. (2021) | 1.07 | 0.84–1.29 | 97.22 | 0.001 |
9 | Simelane et al. (2020) | 1.07 | 0.84–1.29 | 97.84 | 0.001 |
10 | Vong et al. (2021) | 1.02 | 0.80–1.23 | 97.58 | 0.001 |
11 | Mihrete et al. (2014) | 1.08 | 0.88–1.28 | 97.23 | 0.001 |
12 | Sidabalok et al. (2019) | 1.00 | 0.81–1.20 | 97.23 | 0.001 |
13 | Alemayehu et al. (2021) | 1.01 | 0.82–1.21 | 97.35 | 0.001 |
14 | Wilunda & Alessio (2009) | 1.02 | 0.81–1.23 | 97.48 | 0.001 |
15 | Soboksa (2021) | 1.07 | 0.85–1.29 | 97.66 | 0.001 |
16 | Islam et al. (2018) | 1.04 | 0.83–1.25 | 97.63 | 0.001 |
17 | Getahun & Adane (2021) | 1.01 | 0.81–1.20 | 97.25 | 0.001 |
18 | Aluko et al. (2017) | 1.07 | 0.89–1.29 | 96.69 | 0.001 |
19 | Soboksa et al. (2021) | 1.00 | 0.80–1.20 | 97.41 | 0.001 |
20 | Siruri (2013) | 1.03 | 0.83–1.23 | 97.52 | 0.001 |
Publication bias
Funnel plot with 95% confidence limits of the association between unsafe child feces disposal practices and childhood diarrhea.
Funnel plot with 95% confidence limits of the association between unsafe child feces disposal practices and childhood diarrhea.
DISCUSSION
The aim of this study was to pool the available evidence on the extent of unsafe child feces disposal practices and its association with reported diarrhea in children in low- and middle-income countries. According to this systematic review and meta-analysis, the pooled prevalence of unsafe child feces disposal practices in low- and middle-income countries was 52.63% (95% CI: 0.43–0.62). Our study finding is almost similar to a Water Safety Plans (WSP) and UNICEF investigation of 24 countries, which found that over 50% of households in 14 of the 24 countries did not dispose of their children's feces in any type of toilet or latrine; that is, the feces were disposed of unsafely (World Bank Group and UNICEF 2014). Despite the fact that we found a high prevalence of unsafe disposal in our analysis, the sustainable development goal (SDG) number 6, which aims to end open defecation by 2030, is important for reducing unsafe disposal of child feces (Le Blanc 2015; Bárcena et al. 2018).
Generally, children are at a higher risk than adults of getting infected by enteric pathogens when their feces are left in the open. Studies have shown improper disposal of children's feces leads to a greater risk of diarrhea in children under 5 years of age (Gil et al. 2004; Majorin et al. 2014; Bawankule et al. 2017). In the current systematic review and meta-analysis, the risk of diarrhea increased by 4% due to unsafe child feces disposal practices by mothers/guardians even though statistically not significant. Our study finding was supported by a meta-analysis done on children's feces disposal practices, which showed that unsafe child feces disposal practices increased the risk of diarrheal diseases by 23% (Gil et al. 2004). Additionally, our study finding was supported by an intervention study conducted in the city of Bangladesh, which showed a 26% reduction in pediatric diarrhea from improved safe disposal of infant feces, although the amount of risk reduction varied widely (Stanton & Clemens 1987). The possible explanation for the above-observed discrepancy between the current meta-analysis and comparable findings might be due to the difference in the socio-demographic characteristics of the study participants, sample size or study design.
A review of studies found that a considerable number of children's feces were not removed from their original defecation sites, which are responsible for contamination, could be a major cause of diarrhea (Gil et al. 2004). However, in our subgroup analysis of the study, there was no significant association between the presence of diarrhea and unsafe maternal/guardian disposal practices when disposing of children feces in the sub-analysis of studies conducted in African countries. A similar finding was reported by a longitudinal study conducted as part of a randomized controlled trial in rural Bangladesh (Islam et al. 2020). In areas where child feces are not removed from their original defecation sites, the presence of diarrhea may be influenced not only by unsafe stool disposal but also by feeding practices, maternal personal hygiene, and environmental sanitation. This implies that, in addition to sanitation facility improvements, behavior change strategies on feeding practices, maternal/guardian personal hygiene practices, drinking water handling, and proper utilization and increasing latrine access are required.
On the other hand, aggregate studies conducted in Asia showed that the likelihood of diarrhea increased significantly when mothers/guardians engaged in unsafe disposal of infant feces. The results of this subgroup analysis confirm a previous systematic review and meta-analysis which found that unsafe practices for disposing of infant feces increase the risk of diarrheal disease (Gil et al. 2004). This could be because open feces in the compound, as well as wash-off or run-off from precipitation into other compounds and nearby watercourses (unsafe disposal of child feces), can increase the risk of fecal exposure for compound members, particularly young children who spend time in the courtyard area and have hand contact with feces or soil contaminated by feces (fecal pathogens) that cause diarrhea diseases in children (Gil et al. 2004; Kwong et al. 2016). These results indicate the need for further systematic review and meta-analysis of intervention studies on the effects of unsafe child fecal disposal practices on diarrhea in children to examine the relationships between child fecal disposal practices and diarrhea.
We recognized some limitations in this systematic review and meta-analysis. The first concern was the use of English-only articles. Another limitation is that because all studies in this review were cross-sectional, the outcome variable may be affected by other confounding variables. In addition, because the articles included were from a limited number of countries, the pooled prevalence and likelihood OR may not represent the entire population in low- and middle-income countries.
CONCLUSIONS
The pooled prevalence of unsafe child feces disposal practices among mothers/guardians was high in low- and middle-income countries according to this study. This meta-analysis also showed that there was no significant association between unsafe child feces disposal practices and childhood diarrhea. According to the subgroup study, there is no significant link between unsafe child feces disposal practices and child diarrhea in Africa. However, when studies from Asia were pooled, unsafe disposal of child feces was found to be significantly associated with the odds of diarrhea. Non-governmental organizations and government organizations should increase their efforts to reduce unsafe child feces disposal in light of the findings. It is also critical to promote the advantages of proper child feces disposal. Strengthening safe child feces disposal is recommended in Asia to reduce childhood diarrhea, whereas in Africa, it is better to focus on sanitation facility improvements, hygiene, and sanitation behavior change strategies rather than safe child feces disposal. Furthermore, additional systematic reviews and meta-analysis are recommended to assess the link between unsafe fecal disposal practices in children and childhood diarrhea.
ACKNOWLEDGEMENTS
We thank the authors of the studies included in this analysis.
FUNDING
This research received no specific grant from any funding agency in the public, commercial, or not-for-profit sectors.
AUTHORS' CONTRIBUTIONS
N.E.S. conceptualize the review. N.E.S. and D.B.G. extracted data and, with the support of B.N., conducted a meta-analysis. The manuscript was written by N.E.S., B.N., A.E.H., and B.K.O. contributed to the critical review of the manuscript. All authors read and approved the final manuscript.
DATA AVAILABILITY STATEMENT
All relevant data are included in the paper or its Supplementary Information.
CONFLICT OF INTEREST
The authors declare there is no conflict.