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<br />f <br /> <br />. <br /> <br />. <br /> <br />HABITAT CONSERVATION PLANNING: INTRODUCTION <br /> <br />tailor his threatened species regulations in any <br />manner he sees fit. However, his discretion <br />must be grounded in what is necessary for the <br />"conservation" of the species. ESA's definition <br />of conservation is a nearly all-inclusive list of <br />actions that might be taken for the benefit of a <br />species. However, "regulated taking" is <br />authorized under that definition only "in the <br />extraordinary case where population pressures <br />within a given ecosystem cannot be othetwise <br />relieved." Thus, although the Secretary enjoys <br />considerable flexibility in fashioning regulations <br />to fit the needs of threatened species, his <br />authority to allow "regulated taking" of such <br />species is limited. Whether "regulated taking" <br />includes taking incidental to the carrying out <br />of othetwise lawful activities will be examined <br />in more detail later. <br />Before leaving the subject of taking, a word <br />is in order concerning its scope. Historically, <br />most wildlife legislation has used the term <br />"taking" to refer to hunting, fishing, collecting, <br />and similar activities that have as their purpose <br />the killing, or bringing into personal posses- <br />sion, of a wild animal. Gradually, the usage of <br />the term has broadened to encompass still <br />other activities. In the Endangered Species Act, <br />the term "taking" has an extraordinarily broad <br />definition. Most particularly, it includes killing, <br />harassing, or harming a protected animal. No <br />element of intent is included in the definition. <br />Thus, a land developer whose bulldozers crush <br />the larvae of an endangered butterfly on his <br />land commits just as much of a taking as the <br />hunter who deliberately shoots a bald eagle. In <br />fact, it is not even necessary that any en- <br />dangered animal be immediately killed in order <br />for a taking to occur. ESA's definition of <br />taking includes acts that "harm" a species. By <br />regulation, the Fish and Wildlife Service has <br />defined the term "harm" to include habitat <br />modifications that significantly impair essential <br />behavioral patterns and thereby result in actual <br />death or injury to the species. Thus, for ex- <br />ample, the developer who fills in one of the last <br />major breeding ponds of an endangered am- <br /> <br />5 <br /> <br />phibian has likely committed a taking violation <br />even if none of the amphibians is present in <br />the pond at the time of its filling. <br /> <br />THE INTERPIAY BElWEEN <br />SECTIONS 7 AND 9 <br /> <br />The above summaries of Sections 7 and 9 <br />reflect the interpretations and understandings <br />of these provisions that have developed over <br />the 17 -year history of the Endangered Species <br />Act. At the time of ESA's passage, the scope of <br />these provisions and the interplay between <br />them were substantially less well understood. <br />By 1982, however, the accumulated experience <br />under ESA brought pressures for change. <br />One of the concerns that had surfaced by <br />1982 was the apparent trap that Section 9's <br />taking prohibition posed for federal agencies. <br />Although this had never happened in practice, <br />the possibility existed that a federal agency ac- <br />tion could be judged consistent with the re- <br />quirements of Section 7 (that is, it would not <br />jeopardize the continued existence of any <br />species), yet be stymied by the fact that it <br />would result in the "taking" of one or more <br />individuals of that species. This was generally <br />perceived to be an unsatisfactory result because <br />Section 7 had been understood to impose spe- <br />cial, and rigorous, duties on federal agencies <br />that, if met, gave a reasonable assurance that <br />the effects of the federal action on listed species <br />were "acceptable." If any amount of taking, no <br />matter how inconsequential for the overall <br />well-being of a species, could derail a federal <br />project, then the very reason for Section 7 <br />seemed questionable. To fix this dilemma, <br />Congress in 1982 amended the Endangered <br />Species Act to include, as part of the Section 7 <br />consultation process, a mechanism for <br />authorizing any takings that Occur incidental to <br />the carrying out of a federal action that other- <br />wise satisfies Section 7's substantive require- <br />ments. <br />The perception that a problem in need of <br />fixing existed for federal agencies in such situa- <br />