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<br />knowledge about the behavior and habitat requirements of the species to be <br />protec ted. For abundant species, the needed information is either known or <br />can be co llec ted through experiments with management techniques. Often, how- <br />ever, very little is known about the habits of endangered or rare species, and <br />predicting the response of such species to management techniques is very prob- <br />lematical. That is, wildlife management may be more appropriate as a supple- <br />ment to control of development than as a replacement for it. A third reason <br />has to do with the incentives facing an agency with the responsibility of <br />protecting endangered species. The costs of wildlife management come out of <br />the agency's budget, whereas the costs of regulation are paid by the regulatee. <br />With many species to protect and limited resources to do so, an agency has an <br />incentive to export the costs when possible. Therefore, even if substitution <br />of wildlife management is otherwise attractive, it could be thwarted by insti- <br />tutional barriers. <br />3. Distributional Consequences. Protection of endangered species pro- <br />vides benefits to society, but it also imposes costs in opportunities foregone. <br />How are these costs to be distributed? More specifically, given an economic <br />development that must be circumscribed or canceled to avoid impacts on endan- <br />gered species or critical habitat, should the costs of doing so be borne by <br />the developer? <br />From the standpoint of fairness, this is not an altogether easy question <br />to answer. Ownership of land or other resources confers rights which, while <br />not abso lute, are none the less substantial. According to the Constitution, if <br />the government is to prevent those rights from being exercised, the owner must <br />be compensated. In the context of endangered spec ies protec tion, what sorts <br />of landowner activities may be regulated, and what sorts require compensation? <br />Most people would agree, for example, that the killing of endangered species <br />on private land could be regulated without unduly diminishing the value of the <br />property right. But what of "reasonable" use of land, ordinary economic acti- <br />vities that inadvertently affect the habitat of endangered species? Regulation <br />of this sort of activity would, moreover, seem to violate at least one of the <br />canons of equity used in public finance: willingness~to-pay. Application of <br />the willingness-to-pay concept would suggest that the cost of endangered spe- <br />cies protec tion should be borne by the public at large or perhaps by preser- <br />vationists with an especially strong interest in endangered species protection. <br /> <br />8 <br />