jp8589 WRI.qxd - World Resources Institute
jp8589 WRI.qxd - World Resources Institute
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