: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).
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