| Literature DB >> 21085694 |
Jamie Bartram1, Sandy Cairncross.
Abstract
Entities:
Mesh:
Year: 2010 PMID: 21085694 PMCID: PMC2976722 DOI: 10.1371/journal.pmed.1000367
Source DB: PubMed Journal: PLoS Med ISSN: 1549-1277 Impact factor: 11.069
Figure 1Contributions in DALYs of individual diseases to the total burden of ill-health preventable by improvements in HSW.
PEM, protein-energy malnutrition. Source: [1].
Environmental classification of water- and excreta-related infections.
| Category | Examples | Control Strategies |
|
|
| Improve water quality (to prevent water-borne transmission), improve water availability, hygiene promotion (to prevent water-washed transmission) |
|
|
| Improve water availability, hygiene promotion |
|
| AscariasisTrichuriasisHookworm infection | Sanitation, hygiene promotion, treatment of excreta before re-use |
|
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| As C above, plus meat inspection and cooking |
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| Reduce contact with/consumption of infected water, sanitation, treatment of excreta before re-use |
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| Reduce number of potential breeding sites and need to pass near them, improve surface water drainage, use repellent/insecticide where appropriate |
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| Rodent-borne excreted infectionsLeptospirosisTularaemia | Rodent control, hygiene promotion, reduce contact with infected water |
Source: Adapted from [58].
Excreted infections comprise all those in Categories A, C, and D plus helminthic diseases in Category E.
Figure 2Results of reviews of the effect on diarrhoea of HSW interventions.
Results of the previous reviews are for the better quality studies. The reduction for household drinking water connections is in addition to reductions for water quality and availability of public sources. Previous reviews: (a), (c)–(f) [8]; (b) [11]). Fewtrell et al. [57].
Figure 3Determinants of diarrhoea in Salvador, Brazil, 1997–2004: Results of a hierarchical effect decomposition analysis.
The width of each vertical bar shows the proportion of diarrhoea risk attributable to socioeconomic status and mediated by the intermediate variables shown. The two figures show conditions respectively (A) before and (B) after implementation of a major sanitation project. The project was associated with a 21% reduction in diarrhoea citywide, and 42% in the high incidence areas. Socioeconomic status accounted for 23% of the variance in diarrhoea rates before the project, but afterwards the strength of that link had been halved, to 11%. The proportion of that association mediated by intermediate variables, particularly sanitation, was also greatly diminished. Source: [20].
Cost-effectiveness of HSW compared with other public health interventions.
| Intervention | Cost-Effectiveness Ratio(DALYs Averted per US$1,000 Spent) |
|
| |
| Hygiene promotion | 200 |
| Sanitation promotion | 90 |
| Water regulation and advocacy | 12 |
| Cholera or rotavirus immunization | 0.5 |
|
| |
| Condom promotion and distribution | 10–12 |
| Antiretroviral therapy | 1–3 |
|
| |
| Insecticide-treated bednets | 80–140 |
| Intermittent preventive treatment in pregnancy | 120 |
|
| |
| Directly observed short course (DOTS) | 8–90 |
Source: [21].
Figure 4The cost to two national economies of inadequate HSW.
The “direct” effect is mortality attributable to these environmental risk factors, “indirect” effect includes mortality mediated by environmentally caused malnutrition, and “education” includes the effects of that malnutrition on (i) grade attainment; (ii) school achievement (learning productivity) in terms of grade equivalents; (iii) delayed primary school enrolment; and (iv) grade repetition. The latter two effects result in delayed labour force entry. Source: [22].
Proportion of the population of developing countries with access at each level, in 1990 and 2008, to sanitation and water supply.
| Level of Access | Proportion with Access (%) | |
| 1990 | 2008 | |
|
| ||
| Open defecation | 32 | 21 |
| Unimproved | 18 | 14 |
| Shared | 9 | 13 |
| Improved | 41 | 52 |
|
| ||
| Unimproved | 29 | 16 |
| Other improved | 32 | 35 |
| House connection | 39 | 49 |
Notes: “Unimproved” sanitation facilities are those with no hygienic separation of faeces from human contact; e.g. open pit, platform or bucket latrines. “Improved public” water sources include public taps or standpipes, tube wells or boreholes, protected dug wells and rainwater collection. “Piped water at home” means inside the user's dwelling, plot or yard. Source: [4].
Figure 5Health sector functions to secure environmental health.
Source: [43].