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<br />All i1l terests tbat <br />contribute to the <br />problem of <br />endangerment <br />sbould bear an <br />equitable sbare of <br />the recovery} costs. <br /> <br />4 <br /> <br />002H 7 <br /> <br />preservationist basis of endangered species pro- <br />tection, although critical habitat designation is <br />a prominent exception. See Salzman, Evolution <br />and Application of Critical Habitat Under tbe <br />ESA, 14 HARv. ENVTL. L. REv. 311 (1990). <br />The year 1981 began the reign of an ad- <br />ministration that for twelve years resisted any <br />strengthening of endangered species protection <br />law. While it is unclear whether, or to what <br />extent, the federal agencies in that period were <br />able to diminish or circumvent ESA strictures in <br />private consultations, the counterreformation <br />policies of Interior Secretary James Watt clearly <br />failed in wildlife and other namral resource areas <br />when evaluated by judges. See generally Cog- <br />gins & Nagel, "Notbi1lg Beside Remains:" The <br />Legal Legacy fofJames G. Watt), 17 H.C. ENVTL. <br />Me. L. REv. 473 (1990). <br />A few courts gave the government a gen- <br />erous benefit of the doubt in land use versus <br />endangered species cases. E.g., Cabinet MOlin. <br />tains Wilderness v. Peterson, 685 F.2d 678 <br />(D.C. Cir. 1982); Natio1lal Wildlife Fed'n v. <br />National Park Serv., 669 F. Supp. 384 (D. Wyo. <br />1987). Most courts, however, followed the more <br />literal reasoning of the Snail Darter opinion. <br />Thus, the Reagan-Bush administration was <br />thwarted in its attempts to allow SpOrt hunting <br />of wolves in Minnesota, Sierra Club v. Clark, <br />755 F.2d 608 (8th Cir. 1985); to ignore the <br />Act's procedures when the threat from road <br />building was low, Thomas v. Pelerson, 753 <br />F.2d 754 (9th Cir. 1985); to authorize poison- <br />ing that could affect listed species, Defenders <br />of Wildlife v. Administrator, 882 F.2d 1294 <br />(8th Cir. 1989); to sell oil and gas leases with- <br />out ESA compliance, Bob Marshall Alliance v. <br />Hodel, 842 F.2d 1223 (9th Cir. 1988), cert. <br />denied, 109 S. Ct. 1340 (1989); and to eradi- <br />cate red-cockaded woodpecker habitat, Sierra <br />Club v. Yeutter, 926 F.2d 429 (5th Cir. 1991). <br />Human land use became the focal arena for ESA <br />interpretation precisely because habitat de- <br />struction is a more harmful and widespread <br />cause of endangerment than outright killing. <br /> <br />The ESA and Land Use <br /> <br />The Fundamental Conflict. Even though <br />much of the ESA seems targeted narrowly at par- <br />ticular identified species, its scope is necessar- <br />ily and inherently wide. Listing of a species as <br />endangered or threatened, if at all reasonable, <br />is more than a judgment about that species' <br />population status; it is also a finding that one <br />or more things are seriously wrong with that <br />animal's environment. Bald eagles were not just <br />being shot by disgruntled sheepherders, their <br />entire milieu was poisoned by DDT. The re- <br /> <br />NH&e/SUMMER ] 9YJ <br /> <br />cently listed salmon runs were not just being <br />overfished, their riverine (and marine) habitat <br />was in wretched condition from multiple causes. <br />Few want to shoot red.cockaded woodpeckers <br />for sport; their decline is attributable to the <br />conversion of climax forests into monoculture <br />tree farms. When the Fish and Wildlife Service <br />(FWS) lists a species, therefore, an inevitable <br />consequence is that the species not only re- <br />quires direct protective measures (e.g., a ban <br />on taking), but radical or fundamental improve- <br />ments in its habitat as well if the Act's purpose <br />is to be achieved. Such improvements must nec- <br />essarily come from land use controls. <br />Assume, for instance, that the agency lists <br />as endangered a run of salmon that spawn in <br />Idaho. First, controls on commercial, sport, and <br />Indian fishing would be mandatory. Thereafter, <br />if Carson- Truckee Water Conservation Dist. <br />v. Watt, 741 F.2d 257 (9th Cir. 1984), cert. <br />denied, 470 U.S. 1083 (1985), and United <br />States v. Gle1l1l.Colusa Irrigation Dist., 788 F. <br />Supp. 1126 (E.D. Cal. 1992), are good indi- <br />cations, the regulatory focus will fall on water <br />quantity, The responsible agencies and divert- <br />ers would have to devise means to ensure that <br />sufficient water for passage and spawning re- <br />mained in the hundreds of miles of river flow. <br />ing to the ocean. In the next regulatory phase, <br />barriers to passage (e.g., dams, weirs) would <br />come under expansive scrutiny, and retrofitting <br />would be an obvious solution. If these measures <br />did not markedly improve the species' survival <br />rate, agencies or citizens would be forced to <br />look at other causes of decline. When they did <br />so, they would confront a wide spectrum of <br />human activity: timber cutting; agricultural and <br />industrial poisons; livestock grazing; irrigation; <br />mining; recreation; and so on. The causation <br />equation usually is many-factored. All interests <br />that contribute to the problem of endanger- <br />ment, even if their activities are legal, should <br />bear an equitable share of the recovery costs. If <br />comprehensive approaches are adopted, not <br />only will the species rebound, but the entire <br />environment it inhabits will be healthier. <br /> <br />The Rule of Law and the <br />Northern Spotted Owl <br /> <br />Enforcement of the ESA strictures by pri. <br />vate conservation organizations has been, by and <br />large, a triumph of the rule of law. Most of the <br />cases cited above were initiated by private cit- <br />izens. But the current big story, of course, is <br />that ofthe northern spotted owl. The prolonged <br />litigation-still far from over-provides a text- <br />book example of how determined private citi- <br />zens can translate the striCt congressional <br />