<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 />
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