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(HEMA) Initiative. - OAS

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PREVIOUS DOCUMENTS Estimating economic benefits of environmental health interventions within the context of the <strong>HEMA</strong> iniciative<br />

aggregate annual increase in water and sanitation infrastructure and services by US$ 11 billion<br />

above current expenditures results directly in economic benefits that exceed US$ 84 billion per<br />

annum. Assumptions used in this conclusion include calculating the cost of delivery of<br />

decentralized, less-capital intensive water filtration systems installed at the household-level. The<br />

main economic benefit identified is a global decline in diarrheal disease by 10 percent.<br />

The global cost of reducing by half the number of people currently without adequate access to<br />

these services would be US$ 11 billion per year (until 2015), with a per capita annual cost of around<br />

US$ 5. In other words, massive gains could be made with limited amounts of investment. 30<br />

Large variations in the cost-effectiveness of various interventions (across health hazards and<br />

within one type of hazard, such as urban air pollution) point to the need for rigorous analysis and<br />

skillful design of environmental health projects to maximize health benefits in a cost-effective<br />

manner. A recently completed World Bank study of water, sanitation, and health linkages in the<br />

State of Andhra Pradesh in India provides probably the strongest data in support of this point. The<br />

study found that costs per DALY saved from water supply and sanitation interventions vary<br />

greatly, depending on a complex variety of factors, including but not limited to the sociodemographic<br />

situation in a district, the urban or rural status of the community, sanitation<br />

coverage, and type of service delivery. 31<br />

3.1.1 Balancing Priorities through Integrated Policies<br />

Poverty reduction, development, and growth targets hinge, to a large degree, on the extent to<br />

which municipalities, rural communities, agricultural and industrial practices have predictable<br />

access to clean water, adequate wastewater treatment, and sanitation services. Despite the MDGs,<br />

commitments of the UN Commission on Sustainable Development, the World Water Forum, and<br />

elsewhere, national ministries of agriculture, energy, transportation, as well as local authorities<br />

and the private sector, still look for compelling argument to justify investments in clean drinking<br />

water and wastewater treatment services as a core component of development. Numerous studies<br />

show that scarce resources directed at the delivery of clean water, sanitation services and<br />

wastewater treatment accrue direct and substantial economic and social benefit return.<br />

The rationale of integrating water management with other policy areas -including agriculture,<br />

ecology, energy, transportation, governance and public health- has been recognized for sometime.<br />

Integrated water resources management (IWRM) is intended to overcome problems that arise in<br />

the management of watershed basins as a result of bifurcated or uncoordinated policies such as<br />

large-scale hydropower projects that create environmental pressures or input subsidies for<br />

pesticides and agrochemicals, which lead to increasingly high sources of non-point pollution. The<br />

Global Water Partnership (GWP) defines IWRM as a process intended to promote the coordinated<br />

development and management of water, land and related resources.<br />

For an urban water utility, IWRM implies that the utility's water management will be an integral<br />

part of a broader regional or river basin management strategy. The integration of water resource<br />

management should ideally take place across a number of different dimensions, including:<br />

• Upstream management should be integrated with downstream management, so as to ensure<br />

that downstream needs are considered when taking upstream decisions.<br />

• Meeting one demand for water should be balanced against the opportunity costs of not<br />

meeting others, so as to ensure that water is allocated efficiently and equitably.<br />

• The use of water to bear away wastes should be balanced against the impacts this may have<br />

on its capacity to meet other human and environmental demands.<br />

• Managing supplies should be integrated with managing demands, so as to ensure that costly<br />

additions to supply are not undertaken when there are less costly opportunities to reduce<br />

demands.<br />

Meeting of Ministers of Health and Environment of the Americas | 49

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