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Cost Benefit Analysis and <br />Environmental Impact Assessment <br />The decisions which cause impacts in wetlands <br />are often very old and well established. The <br />disappearance of the upper reaches of River Ver in <br />the permeable chalk-based Chiltern Hills of <br />England derives in large part from the granting of <br />a license to construct a huge well near the river <br />in 1952 (Halcrow 1988). The maximum abstraction <br />was set at the estimate of rainfall minus actual <br />evapotranspiration. During those post-war years of <br />reconstruction, the arrival of a major U.S. motor <br />manufacturer in the nearby town was a cause of <br />national celebration. Today, as the pumping from <br />the well finally reaches the permitted maximum, <br />there is a major campaign to save the spring-fed <br />meadows, the special chalk stream ecology and the <br />landscape of the river. The major problem facing <br />the community group endeavoring to save the valley <br />bottom wetlands is that licences, issued before <br />the passage of the 1963 Water Resources Act, were <br />made indefinite "licences of right" by that <br />legislation. <br />Wetlands are often ignored in the formulation <br />of water resource schemes and river basin <br />management strategies. Sadly, the 1975 Plan <br />Directeur des Eau du Nord de Is Tunisie and <br />subsequent elaborations of that scheme (Direction <br />EGTH 1982) have completely ignored the existence <br />downstream of the Ichkeul National Park. This has <br />designations under Ramsar, World Heritage and <br />Biosphere Reserve conventions as well as a major <br />fishery and nationally significant grazing lands. <br />In principle, cost-benefit analyses should only <br />permit rational decision making and should protect <br />wetland resources from ill-conceived degradation. <br />However, it is often the case that these analyses <br />are organised to favour traditional forms of <br />capital-intensive "development". For example, it <br />is often assumed that the current prices for the <br />products of the scheme will remain at what are <br />often record levels; all of the farmers are <br />assumed to adopt the new systems of cultivation <br />whilst none of the farmers is assumed to be likely <br />to increase production without the implementation <br />of the large scheme; and socio-economic factors <br />such as the employment situation, the transport <br />network and systems of land ownership are always <br />assumed to work perfectly in the post-scheme <br />world. Adams and Hollis (1989) showed that, for <br />the 14,000 ha Kadawa irrigation scheme near Kano <br />in Nigeria, the ratio of production to cost <br />declined from 13:1 in 1984 to 2.7:1 in 1986. <br />However, the true ratio would be much more <br />unfavourable because the 180 million naira of <br />capital costs was regarded as sunk capital; the <br />repayment of loans in foreign currency was ignored <br />even though the scheme produced very little that <br />could be exported or used for import substitution; <br />the gross figures for farmers' production ignored <br />labour cost and other inputs by the farmers; and <br />the scheme was actually costing the government <br />6.16 million naira a year to operate. <br />Environmental impact assessment (EIA) is often <br />seen as a solution to all of the problems of <br />wetland degradation. However, it is essentially a <br />negative technique which is often seen to block or <br />delay development. By its very nature it is almost <br />always concentrated on large schemes whilst small <br />projects or decisions by individuals at a micro- <br />scale can easily evade the rigour of EIA. Sadly, <br />it is possible for developers to "buy" or to bias <br />environmental impact assessments. For instance, <br />the Greek government contracted a single member of <br />the Hellenic Ornithological Society to undertake <br />an EIA on the effects of the major Achelos River <br />diversion scheme on the downstream coastal lagoons <br />at Messalonghi. The resulting study has not been <br />accepted by the Hellenic Ornithological Society <br />and the whole episode has generated fundamental <br />divisions in the small conservation community in <br />Greece. <br />In many circumstances EIA is not undertaken. In <br />situations where a good study is completed, the <br />EIA is frequently ignored because of what are <br />perceived to be overriding national priorities. <br />EIA on its own is not sufficient to protect <br />wetland resources. It can only be one element <br />within a much broader strategy which seeks to <br />promote the positive benefits of wetlands rather <br />than concentrating on the negative review of <br />projects. The Ramsar Bureau's working group on <br />criteria and wise use has drafted such a broad- <br />based strategy for consideration at the next <br />Conference of the Contracting Parties (Ramsay <br />Bureau 1988). <br />Factors Affecting Management <br />The fact that wetlands are still viewed as <br />wastelands in many parts of the world represents <br />twin failures on the part of the "wetlands <br />community". First, there has been a failure to <br />demonstrate the functions and values of wetlands <br />in many countries of the world. Second, the <br />communication of the functions and values of <br />wetlands to the public and politicians has been <br />deficient in large areas of the globe. The U.S. <br />experience in both functional analysis (National <br />Wildlife Federation 1987) and its dissemination to <br />decision makers (Conservation Foundation 1988) <br />will be invaluable in the campaign to conserve <br />wetlands worldwide. <br />There are public subsidies both overt and <br />covert for wetland destruction. In Tunisia, until <br />the last few months, the government paid all the <br />cost of pumping drainage water from low-lying <br />fields. Such a policy naturally causes wetlands to <br />shrink rapidly in the face of agricultural <br />expansion. In Greece, the price of electricity for <br />pumping irrigation water from wells is set at 25% <br />below the normal price. This covert policy has the <br />effect of lowering water table levels, as at the <br />site of former Lake Karla between Volos and <br />Larissa. <br />International funds still appear to be plenti- <br />ful for projects which result in wetland destruc- <br />tion. The World Bank, (Cleave 1988) has certainly <br />taken a lead in establishing a division to deal <br />with environmental issues and it is now widely <br />acknowledged as a green-edged organization. Most <br />of the financial institutions responsible for <br />foreign aid from the Federal Republic of Germany <br />22