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Last modified
7/14/2009 5:02:30 PM
Creation date
5/20/2009 5:14:13 PM
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UCREFRP
UCREFRP Catalog Number
7393
Author
Harrington, W.
Title
Endangered Species Protection and Water Resource Development.
USFW Year
1980.
USFW - Doc Type
LA-8278-MS,
Copyright Material
NO
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<br />2. Efficiency. A very effective preservation policy would be to stop <br />all development from proceeding until exhaustive biological studies are done, <br />and then permit only those activities for which there is no chance that endan- <br />gered wildlife will be harmed. Let us call this a "maximal preservation pol- <br />icy." Such a policy has never been seriously considered because society and <br />its members have other objectives besides the preservation of endangered spe- <br />cies. This means that decisions must be made with respect to "how much" of <br />each objective is to be purchased with society's limited resources. Advocates <br />of particular objectives are often offended by the notion that such tradeoffs <br />are necessary. According to this position, there is no way to place a value <br />on human life or, more to the point, a species of wildlife. However, the very <br />fact that a maximum preservation policy will not be entertained places, albeit <br />implicitly, a maximum valuation on endangered species protection though its <br />estimation may be difficult if not impossible. <br />Ideally, tradeoffs among competing objectives are made to enter social <br />dec isionmaking in the budgetary process. Inasmuch as one rarely knows the <br />relationship between budgetary inputs and program outputs (effectiveness) these <br />tradeoffs must necessarily be very rough. Moreover, even this rough budgetary <br />balancing process is not available for agencies with significant regulatory <br />responsibility because the cost of their regulations are not borne by them but <br />by those regulated. There is a certain irony here. The need for regulation <br />to protect endangered species in the first place arises from the fact that the <br />effects of water resources development on endangered species is an exter- <br />nality. An agency whose only responsibility is endangered species protection <br />in turn imposes externalities on developers (who may, as it happens, be other <br />federal agencies). Socially efficient decisions require that both types of <br />external effects be considered simultaneously, but to devise institutions <br />permitting this is no easy task. Ordinarily, the courts provide the only <br />means whereby such objectives are balanced, but the transaction costs of this <br />approach are high.* <br />Efficiency concerns do not end with the balancing of various policy <br />objectives. One must also be concerned with cost-effectiveness: given an <br /> <br />*The 1978 Amendments to the Endangered Species Act provide another approach <br />for really hard cases: the Endangered Species C01IIIlittee, whose operation is <br />discussed below. <br /> <br />6 <br />
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