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jp8589 WRI.qxd - World Resources Institute

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CHAPTER 4<br />

FOUR STEPS TO ENVIRONMENTAL INCOME<br />

TABLE 4.2 PAYMENTS FOR ENVIROMENTAL SERVICES<br />

Locale<br />

Costa Rica<br />

Pimampiro, Ecuador<br />

Cauca Valley, Columbia<br />

Kerala, India<br />

Botswana, Kenya,<br />

Namibia, South Africa,<br />

Tanzania, Zimbabwe<br />

Scholel Té, Chiapas, Mexico<br />

Enviromental Service<br />

Forest conservation and<br />

reforestation for watershed<br />

maintenance and carbon storage<br />

Forest protection of headwaters to<br />

ensure clean water supply for the town<br />

Forest management to improve<br />

stream flows and reduce sedimentation<br />

of irrigation canals<br />

Discovery and maintenance of a<br />

continued supply of Jeevani, a<br />

commercially marketed medicine<br />

Support of ecotourism in southern<br />

and eastern Africa through the maintenance<br />

of landscapes, natural<br />

resources, and wildlife habitat<br />

Forest management leading to carbon<br />

sequestration<br />

Value to Community<br />

More than US$100 million disbursed under 10-15 year contracts with over<br />

450,000 ha enrolled in program. Funded by a fuel tax and contributions from<br />

private companies.<br />

Rodriguez 2004<br />

$1 per hectare payments constitute 30% of income for those households<br />

participating in forest protection.<br />

Grieg-Gran and Bishop<br />

US$1.5 million invested in poor communities in the upper watershed by<br />

downstream farmers.<br />

Scherr et al. 2004<br />

500-1000 families will earn wage income from cultivation and harvesting of<br />

the fruit and leaves that are used to manufacture the drug. Ongoing royalty<br />

payments to the community from drug sales.<br />

Landell-Mills and Porras 2002<br />

Direct employment of 3000 people; over US$100,000 reinvested in local<br />

economic development and conservation activities.<br />

Landell-Mills and Porras 2002<br />

Two-thirds of the value from the sale of carbon contracts goes to farmers. In<br />

2002, US$120,000 was distributed to 700 participants.<br />

IUCN 2003<br />

ecosystem services have a quantifiable economic value. If people<br />

downstream are being regularly flooded, the ability of the intact<br />

forest to moderate stream flows and lessen the flood risk will be<br />

worth something to them, and they may be willing to pay the<br />

upstream forest owners to preserve and protect this service—or<br />

even to restore it.<br />

In the last decade or so, markets based on this kind of interchange—called<br />

payment for environmental services (PES)—have<br />

begun to develop worldwide. (See Table 4.2.) The most<br />

common environmental services marketed so far have been<br />

associated with forests and fall into four categories: watershed<br />

services like those described above, carbon storage, biodiversity<br />

conservation, and preservation of landscape beauty. Since the<br />

poor are the stewards of many rural ecosystems, it makes sense<br />

that they should be able to tap these payments for environmental<br />

services (PES) as an additional source of environmental<br />

income—another element of their “nature portfolio.” In a few<br />

cases, they have been successful in doing so. But for the most<br />

part, the markets for environmental services, which are still in<br />

their infancy, do not yet serve the poor well.<br />

Deals involving PES range in scale from local to international<br />

and are undertaken by a range of actors, including private<br />

companies, NGOs, communities, and state governments. Private<br />

businesses that depend on natural resources are sometimes<br />

willing to pay for protection of ecosystems, usually following<br />

signs that a resource is threatened or already in decline. In one<br />

promising example in Colombia’s Cauca Valley, downstream<br />

sugarcane growers hurt by flooding paid upland communities—<br />

predominantly poor—to change their land management<br />

practices to protect the watershed. This evened out the water<br />

supply on the valley sugarcane farms and reduced crop damages,<br />

while bringing public benefits—clean water supply, sanitation,<br />

and other economic development projects—to the upland<br />

communities. (See Box 4.4.)<br />

Payments for preserving biodiversity and landscape<br />

beauty often come from conservation NGOs or local businesses<br />

involved in ecotourism. For example, Rainforest Expeditions, a<br />

private company in southeastern Peru, signed a 20-year agreement<br />

with the local Infierno community, splitting profits and<br />

management of the business in return for preservation and<br />

access to the forest and wildlife on the community’s lands<br />

(Landell-Mills and Porras 2002:166).<br />

Governments often act as originators or participants in<br />

PES schemes. In 1996 the Costa Rican government became a<br />

leader in PES when it established the first national program to<br />

dispense payments to farmers willing to maintain or restore<br />

forest ecosystems and their services. The program pays<br />

landowners to reforest their lands or conserve forest lands they<br />

already own, rather than convert them to pasture. By 2004,<br />

more than 450,000 hectares were included in the program, and<br />

107

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