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<br />.' . ". _'. ' " ,_,', .', - .', ',' ._",. ,_-~::,,,,-,,-~,,_~.,::,~;,;,,_o_, . <br /> <br />I. Introduction <br /> <br />The Endangered Species Act (Act) of 1973, as amended, assigns the U.S. Fish and Wildlife <br />Service (Service) the responsibility for listing species of plants and animals in the United <br />States whose existence is either threatened or endangered. After a species is listed, the Service <br />is responsible for, among other things, developing recovery plans, reviewing proposed federal <br />actions to ensure that they do not compromise recovery efforts, and designating critical habitat <br />for listed species. Such critical habitat designations, at least in certain situations, can alter <br />economic activity in critical habitat areas that might otherwise be of detriment to cenain <br />species. <br /> <br />Although the Act has no provisions for studying the economic consequences of listing <br />threatened and endangered species, it does require the Service to assess the economic impacts <br />of all proposed critical habitat designations. As a result, economists have been participating in <br />the ongoing process of designating critical habitat for endangered species and assessing the <br />economic impacts of such designations. 1 <br /> <br />It is almost axiomatic that setting aside critical habitat for endangered species involves a <br />reallocation of resources. Threatened and endangered species are usually listed because the <br />current allocation of resources has resulted in excessive habitat degradation. Such adverse <br />modification of natural habitat is generally due to economic activity that has occurred as a <br />result of human settlement and economic development. Resources are allocated to particular <br />uses as a result, and stabilizing and/or reversing this development requires that these resources <br />be allocated to other uses. For example, trees may not be harvested that provide habitat for <br />birds, water may not be used for irrigation so that stream flows are returned to more historic <br /> <br />I It has been argued that the process of listing a species as endangered or threatened has far greater <br />economic consequences than subsequent critical habitat designations, an argument that has some merit with respect <br />to the examples discussed in this paper. As a practical matter, however, most economic studies of critical habitat <br />designations attempt to estimate the combined effects of both listing and critical habitat designations, and then <br />allocate a proportion of effects to each administrative action. <br /> <br />3 <br />