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:i <br /> 13 ERC 1126 Vational Wildlife Federation v. Gorsuch _ <br /> 3. Policy Considerations forms of NPDES limits (x°ro reduction in <br /> Finally, as a policy matter (and recog- biochemical oxygen demand (BOD) or y <br /> nizing our limited role in reviewing agen- Pounds of BOD Per ton of industrial <br /> cy policy decisions) we are not convinced output) would entail major costs at one <br /> that EPA's decision to leave dam regula- dam, and only minor costs at another. <br /> cion to the states was so misguided as to Thus, is would be difficult at best for EPA <br /> frustrate congressional policy. EPA con- to determine what level of reduction is <br /> obtainable by using the "best available <br /> tends that requiring permits for <br /> 2,000,000 dams would be an impossible technology economically achievable <br /> task. Yet, so far as the record shows, ry for <br /> S C each "category or class" of polluter. <br /> Act §301(b)(2)(.�), 33 <br /> most, if not all of the dams that cause Clean Water <br /> water quality problems are large hydro- U.S.C- § 1311(b)(2)(A) (emphasis added). <br /> electric dams. Thus, the number of dams Control that is economically feasible at <br /> that would require permits is probably no one site may be infeasible at another.76 <br /> more than the 50,000 "large" dams in the Conversely, major expenditures might be <br /> countrY,73 and quite possibly only the required for dams where, say, dissolved <br /> ! 3,000 or so dams that are large enough to oxygen levels are slightly reduced imme- <br /> generate significant amounts of hydro- diatelv below the dam, but not enough to <br /> harm fish, and the river is fully reaerated <br /> electric power.74 That is a manageable <br /> number even if it turns out to be imprac- within a few miles. <br /> tical to issue categorical permics.75 Nor Finally, we cannot say, on the record <br /> are we persuaded by EPA's argument that before us, that federal intervention is . <br /> because the NPDES program requires needed because the states have abdicated <br /> discharge of pollutants to be eliminated their §208 responsibility over a truly <br /> to the extent technologically feasible, it pressing national problem. The record <br /> will preclude beneficial dam-caused water does not show how vigorous state en- <br /> changes, such as cold water discharges to forcement has been, but at least some <br /> j support a trout fishery. It should be efforts have been made to remedy dam- <br /> feasible for EPA to define "pollutant" to caused pollution.77 Supersaturation and <br /> exclude beneficial water quality changes. sediment releases appear to be minor <br /> On the other hand, dam-caused pollu- problems. As discussed earlier, tempera- <br /> ture' Lion is unique because its severity de- changes are not always harmful, are <br /> not easily controllable at single-ou <br /> pends partly on whether other sources tlet have polluted the upstream river. The dams, and can apparently be readily <br /> controlled at multiple-outlet dams. Low <br /> NPDES program, however, requires EPA <br /> t dissolved oxygen and dissolved minerals <br /> o issue nationally uniform standards, <br /> and nutrients are the most serious prob- <br /> and thus would not allow the agency to lems, but EPA has the authority, when it <br /> take full account of the interrelationship <br /> reviews state water pollution control <br /> between dam-caused pollution and other <br /> pollution sources. :�loreover, dams area plans, to insist if need be on stronger <br /> efforts in the future. Also, new dams <br /> major component of state water manage- <br /> meat, providing irrigation, drinking wa- <br /> ter, flood protection, etc. In light of these stl:e water quality requiremeacs; thus the <br /> complexities, which the NPDES program problem is largely limited to existing <br /> was not designed to handle, it may well dams.78 <br /> be that state areawide water quality plans 76 Control costs will also vary from one <br /> are the better regulatory tool. industrial plant to another.As Congress recog- <br /> Also, the severity of dam-caused pollu- nized in requiring cost-benefit analysis only for <br /> tion is highly site-specific. Common each class or category of sources and not for <br /> each individual source, some inefficient plants <br /> 73 Joint Statement of Material Facts, supra may be forced to dose. See E.I. du Pont de <br /> note 4, 13,J.A. at 26. Nemours &Co. v.Train,430 U.S. 112, 128-33 <br /> 74 National Wildlife Federation, Petition for (197 7) (discussing legislative history of$301). <br /> ' Rulemak:ng under the Federal Water Pollution Con- But apparently variation in the cost of pollu- <br /> trol Act 1 (Feb. 28, 1978),J.A.at 117. cion control is likely to be less at industrial <br /> 73 Cf. Natural Resources Defense Council, plants than at dams. Also, one cannot simply <br /> Inc. v. Costle, 568 F.2d 1369, 1380-82 (D.C. shut down an old dam; environmental effects <br /> Cir. 1977) (rejecting EPA claim that it would will remain. <br /> be infeasible to issue permits for 400,000 77 See note 9 supra;note 78 infra. <br /> a¢ricultural and silvicultural point sources). 78 See §401(a)(2), 33 U.S.C. $ 1341(a)(2). <br />