NATURAL RESOURCES DEFENSE COUNCIL, INC., Petitioner, v. U.S. ENVIRONMENTAL PROTECTION AGENCY and Lee M. Thomas, Administrator, U.S. Environmental Protection Agency, Respondents,
Chemical Manufacturers Association, American Iron & Steel Institute, Edison Electric Institute, et al., Cincinnati Gas & Electric Co., et al., Tenneco Oil Company, et al., Atlantic Cement Company, Inc., et al., National Coal Association, General Motors Corporation, Ford Motor Company, Alabama Power Company, et al., American Wood Preservers Institute, Intervenors. No. 80-1607.Footnote *
United States Court of Appeals, District of Columbia Circuit.
Argued March 3 and 4, 1986.
Decided June 30, 1987.
____________________
* AND CONSOLIDATED CASE NOS. 80-1660, 801723, 80-1740, 80-1809, 80-1837, 80-1875, 801881, 80-1889, 80-1909, 80-1914, 80-1923, 801927, 80-1929, 80-1931, 80-1933, 80-1966, 801970, 80-1975, 80-1978, 80-1984, 80-1987, 801989, 80-2002, 80-2007, 80-2114, 80-2279, 811569, 81-1570, 81-1571, 81-1572, 81-1573, 811574, 81-1575, 81-1576, 81-1577, 81-1578, 811579, 81-1708, 81-1709, 81-1746, 81-1747, 811748, 81-1749, 81-1750, 82-1563, 84-1505, 841615, 84-1620, 84-1621, 85-1009, 85-1010, 851017, 85-1018, 85-1019, 85-1024, 85-1025, 851067 and 85-1128.
Precydent - copyright material removed
Petition for Review of Orders of the Environmental Protection Agency.
Theodore L. Garrett, Washington, D.C., William B. Ellis, Richmond, Va., James K. Jackson, Washington, D.C., Robert E, Holden, New Orleans, La., Kristy A. Nichaus, and Robert A. Emmett, with whom Michael K. Glenn, Washington, D.C., Gene W. Lafitte, George J. Domas, New Orleans, La., Raiph M. Mellom, Seth A. Goldberg, Washington, D.C., George W. House, Greensboro, N.C., Corinne A. Goldstein, Joseph M. Fisher, Michael B. Barr, Edwin H. Seeger, Carl B. Nelson, Jr., Washington, D.C., Robert J. Wise, Turner T. Smith, Jr., Richmond, Va., and Stark Ritchie, Washington, D.C., were on the joint brief for industry petitioners, American Petroleum Institute, et al. in Nos. 80-1607, et al. Ronald J. Wilson and Roger S. Greene, with whom James Tayler Banks, Washington, D.C., were on the briefs for environmentalist petitioners, Natural Resources
Defense Council, Inc. and Citizens for a Better Environment in Nos. 80-1607, et al.
Lawrence R. Liebesman, Atty., Dept. of Justice, Ellen Siegler, and Karen M. Wardzinski, Attys., E.P.A. and Elliott P. Laws, Atty., Dept. of Justice, with whom Alan W. Eckert, Senior Litigator, E.P.A. and Dean K. Dunsmore, Atty., Dept. of Justice, Washington, D.C, were on the brief for respondents in Nos. 80-1607, et al.
Elizabeth Stein, Lloyd Guerci, Washington, D.C, Donald W. Stever, Jr., Stamford, Conn., Lee R. Tyner, David T. Buente, Jr., James W. Moorman, and Tony Z. Roisman, Attys., Dept. of Justice, Mark D. Gordon, Richard G. Stoll, Jr., and Todd Gulick, Attys., Environmental Protection Agency, Washington, D.C, also entered appearances for respondents in Nos. 80-1607, et al.
Kristine L. Hall, Washington, D.C, entered an appearance for the Environmental Defense Fund in Nos. 80-1607, et al.
John McN. Cramer, Pittsburgh, Pa., William C. Brashares, Thomas H. Truitt, Charles C. Abeles, David B. Weinberg, Greer S. Goldman, Charles M. Darling, IV, J. Patrick Berry, Stephen L. Teichler, Benjamin W. Boley, Michael S. Giannotto, Washington, D.C., Louis E. Tosi, Toledo, Ohio, and Julius J. Hollis, Detroit, Mich., entered appearances for industry petitioners in Nos. 80-1607, et al.
Thomas M. Lemberg and Leonard A. Miller, Washington, D.C, entered appearances for petitioner, The Ferroalloys Ass'n, in No. 80-1723.
Bill Forcade, Chicago, 111., entered an appearance for petitioners, Citizens for a Better Environment, et al., in No. 80-1740.
Kenneth A. Strassner entered an appearance for petitioner, Kimberly-Clark Corp., in No. 80-1809.
Joseph H. Price and Roger Strelow, Washington, D.C, entered appearances for petitioner, Antex Fibers, Inc., in No. 801837.
Richard H. Caldwell, Houston, Tex., and Richard E. Powers, Jr., Washington, D.C, entered appearances for petitioners, American Petroleum Institute, et al., in Nos. 801875 and 80-1881.
William R. Weissman, Washington, D.C, entered an appearance for petitioners, Edison Elec. Institute, et al., in No. 80-1889.
John R. Quarles, Jr. and Kenneth A. Rubin, Washington, D.C, entered appearances for petitioner, Stablex Corp., in No. 80-1909.
Peter J. Nickles, Charles H. Montange and Kenneth E. Carroll, Washington, D.C, entered appearances for petitioners, KerrMcGee Nuclear Corp., et al., in No. 801914.
Walter G. Talarek, Reston, Va., entered an appearance for petitioner, American Wood Preservers Institute, in No. 80-1923.
James R. Walpole, Roberta L. Halladay, Washington, D.C, and John D. Fognani, Denver, Colo., entered appearances for petitioners, American Mining Congress, et al., in Nos. 80-1927 and 80-1987.
Edward H. Forgotson and Lisa Anderson, Washington, D.C, entered appearances for petitioner, Texas Oil and Gas Corp., in No. 80-1929.
Jonathan Z, Cannon and Karl S. Bourdeau, Washington, D.C, entered appearances for petitioner, Dow Chemical Co., in Nos. 80-1933 and 80-1984.
John B. Fahey, East Hartford, Conn,, entered an appearance for petitioners, United Technologies Corp., et al., in No. 801966.
Louis E. Tosi, Toledo, Ohio, Julius J. Hollis and Leonard F. Charla, Detroit, Mich., entered appearances for petitioner, General Motors Corp., in Nos. 80-1970 and 81-1747.
Clare Dalton, Washington, D.C, entered an appearance for petitioners, Chemical Manufacturers Ass'n, et al., in No. 801975.
Robert V. Percival, Washington, D.C, entered an appearance for petitioner, Environmental Defense Fund, Inc., in No. 801978.
R. Brooke Jackson and John D. Austin, Jr., Washington, D.C, entered appearances
for petitioners, American Min. Congress, et al., in No. 80-1987.
William L. Rosbe, Richmond, Va., entered an appearance for petitioner, Ford Motor Co., in No. 80-1989.
Norton F. Tennelle, Jr. and Lester Sotsky, Washington, D.C., entered appearances for petitioner, Amax, Inc., in No. 80-2002.
Blake A. Biles, Washington, D.C., entered an appearance for petitioner, Lubrizol Corp., in No. 80-2007.
Bill Forcade, Chicago, 111., entered an appearance for petitioners, Citizens for a Better Environment, et al., in Nos. 80-2114 and 82-1563.
Alfred V.J. Prather, Washington, D.C., entered an appearance for petitioner, Kennecott Corp., in No. 80-2279.
George C. Freeman, Jr., Richmond, Va., and J. Thomas Wolfe entered appearances for petitioners, Virginia Elec. & Power Co., et al., in No. 81-1569.
Robert E. Payne and David E. Evans, Richmond, Va., entered appearances for petitioners, American Paper Institute, et al., in No. 81-1573.
Arnold S. Block, Washington, D.C., entered an appearance for petitioners, American Petroleum Institute, et al., in Nos. 811577 and 81-1709.
Larry B. Feldcamp, Houston, Tex., entered an appearance for petitioner, Pennzoil Co., in No. 81-1708.
T.S. Ellis, III, Richmond, Va., entered an appearance for petitioner, Ford Motor Company, in No. 81-1748.
Daniel A. Masur, Pittsburgh, Pa., entered an appearance for petitioners, American Iron & Steel Institute, et al., in No. 85-1009.
Lewis T. Smoak, Greenville, S.C., entered an appearance for petitioner, American Textile Mfrs. Institute, Inc., in No. 851017.
Charles D. Ossola, Washington, D.C., entered an appearance for petitioner, National Coal Ass'n, in No. 85-1024.
Charles S. Mullen, Seattle, Wash., entered an appearance for petitioner, Wyckoff Co., in No. 85-1067.
Before ROBINSON, SCALIA," and STARR, Circuit Judges.
Opinion for the Court filed by Circuit Judge STARR.
STARR, Circuit Judge: The objective of the Clean Water Act is to "restore and maintain the chemical, physical, and biological integrity of the Nation's waters." 33 U.S.C. § 1251 (1982). Under the Act, the discharge of any pollutant into the navigable waters of the United States is unlawful. Id. § 1311(a). This basic rule admits of a critical exception' the discharge of pollutants is permitted if the source obtains and complies with a permit that limits the amounts and kinds of pollutants which can lawfully be discharged. Thus, the cornerstone of the Clean Water Act's pollution control scheme is the National Pollution Discharge Elimination System (NPDES) permit program, established under the Federal Water Pollution Control Act Amendments of 1972. See 33 U.S.C. § 1342 (1982).
The original regulations implementing the NPDES program were promulgated by the Environmental Protection Agency in 1972 and 1973. Prompted by its experience during the "first round" of permitting, as well as statutory changes wrought by the Clean Water Act Amendments of 1977, EPA comprehensively revised the NPDES regulations in 1979. 44 Fed.Reg. 32,854 (June 7, 1979). Petitions for review of these regulations were filed in this and other circuits by numerous challengers, including trade associations, corporations, the Natural Resources Defense Council (NRDC), and Citizens for a Better Environment (CBE). Eventually, all petitions for review of both sets of regulations were
____________________
** Judge (now Justice) Scalia was a member of the panel at the time this case was argued, but did not participate in this opinion.
673 F.2d 392 (D.C.Cir.1980), cert, denied sub nom. Chemical Manufacturers Association v. EPA, 459 U.S. 879, 103 S.Ct. 175, 74 L.Ed.2d 143 (1982); Virginia Electric and Power Co. v. EPA,
655 F.2d 534 (4th Cir.1981).Footnote 1 At that time, the litigants identified about 55 issues under challenge. See Status Reports of Industry NPDES Petitioners, Respondents, and NRDC and CBE (filed Sept. 14, 1981).
After almost two years of settlement negotiations, EPA and the industry representatives (Industry) entered into an NPDES Settlement Agreement (Agreement) (filed June 9, 1982) covering 27 of 47 issues raised by Industry's challenge.Footnote 2 In the wake of this development, our court remanded the record to the agency to permit implementation of the Agreement. Order (Aug. 6, 1982). After notice and comment, EPA promulgated final revisions to the NPDES regulations. 49 Fed.Reg. 37,997 (Sept. 26, 1984). By virtue of the Agreement, Industry signatories were free to renew their challenges to the extent that the final regulations were not substantially the same as or altered the meaning of the terms of the Agreement. Because the final regulations reflected various changes from the Agreement, another flurry of petitions for review, both new and amended, were filed and consolidated in this court.
This opinion addresses the various challenges mounted by the Industry petitioners, on the one hand, and NRDC, on the other, to regulations which (1) define "new source"; (2) grant a ten-year grace period to new sources from more stringent technology-based standards of performance; (3) require permit applicants to identify all toxic pollutants used or manufactured in the industrial process; and (4) prohibit "bypasses," that is, diversions of waste streams from effluent treatment facilities. Finally, we address petitioners' challenges to an issue arising under both the Clean Water Act and the National Environmental Policy Act of 1969 (NEPA), 42 U.S.C. §§ 43214347 (1982)'whether EPA may ban the construction of new sources pending issuance of a permit.Footnote 3 For the reasons that follow, we deny the petitions for review on each of these issues save for the construction ban.
I
The fundamental premise of the Clean Water Act is that "the discharge of any pollutant by any person shall be unlawful" except as otherwise permitted under the Act. 33 U.S.C. § 1311(a) (1982). A "discharge of a pollutant" is defined, in pertinent part, as "any addition of any pollutant to [the waters of the United States] from any point source." Id. § 1362(12)(A). The term "pollutant" is broadly defined to include, among other things, solid waste; industrial, municipal, and agricultural waste; sewage sludge; biological or radioactive materials; wrecked or discarded equipment; heat; rock; sand; and cellar dirt. Id. § 1362(6). A "point source" is "any discernible, confined and discrete conveyance." Id. § 1362(14).
Thus, the Act allows the discharge of pollutants from a point source only in compliance with limitations established in the Act. The Act imposes effluent limitations Footnote 4 through two programs. The first applies water-quality based standards. Id. § 1313. It imposes on a point source effluent limita-
____________________
1. This court has jurisdiction to review these regulations under section 509(b)(l) of the Clean Water Act, 33 U.S.C. § 1369(b)(l) (1982). Natural Resources Defense Council, Inc. v. EPA,
673 F.2d 400, 403 (D.C.Cir.), cert, denied sub nom. Chemical Manufacturers Ass'n v. EPA, 459 U.S. 879, 103 S.Ct. 175, 74 L.Ed.2d 143 (1982).
2. NRDC and CBE were not parties to that agreement.
3. The issues to be addressed in other opinions by the court include three NEPA issues (effluent limits, non-water quality related conditions, admission of evidence); various procedural issues (public participation, APA continuance, non-adversary panel procedures, maximum state penalties, veto authority); storm water issues; toxicity limits; and three issues identified by the parties as "exceptions" (backsliding, net/gross, and upsets).
4. Effluent limitations consist of restrictions on quantities, rates, or concentrations of pollutants and compliance schedules for the achievement of such restrictions. See id. § 1362(11).
tions that are based on the amounts and kinds of pollutants in the water in which the point source discharges. Id. § 1312(a). The second applies technology-based standards. It imposes on a point source effluent limitations based on how much of a reduction technology can achieve. Id. §§ 1311(b), (e), 1314(b).
To describe briefly the second approach, technology-based effluent limitations, as their name suggests, derive from standards formulated with reference to pollution control technology. See id. § 1314(b). The standard applicable in a particular case depends on the kind of pollutant'toxic, conventional, or non^conventional Footnote 5 whether the point source is a new or existing source. Footnote 6
Under section 301, existing sources must achieve effluent limits on nonconventional pollutants that reflect the reduction in effluents that can be achieved through "the application of the best available technology economically achievable." Id. § 1311(b)(2)(A). This is known as the "BAT" standard. New sources, on the other hand, are subject to stricter effluent limitations with respect to nonconventional pollutants. Section 306 prescribes new source performance standards (NSPS) that must reflect the "best available demonstrated control technology." Id. § 1316(a)(l). This more stringent standard for new sources is known as the "BACT" standard. Footnote 7
Toxic pollutants, whether from new or existing sources, are subject to effluent limitations based on application of the BAT standard. Id. § 1317(a)(2). Finally, by 1984 new and existing sources were to achieve effluent reductions in "conventional" pollutants that reflect the application of the "best conventional pollutant control technology," known as a "BCT" standard. Id. §§ 1311(b)(2)(E), 1314(a)(4),
In addition to technology-based standards, Section 302 of the Act provides for water-quality related effluent limitations. These limitations supplement technologybased standards and protect specific bodies of water. Id. § 1312. Whenever a technology-based effluent limitation is insufficient to make a particular body of water fit for 'and on the uses for which it is needed, the EPA is to devise a water-quality based limitation that will be sufficient to the task. Id. § 1312(a).
These national standards establish a nationwide floor for the achievement of pollution control. At the same time, the Act contemplates the delegation of pemit-writing and enforcement authority (as well as some standard-setting authority) to the several States. To date, thirty-seven States have assumed responsibility for issuing NPDES permits.
Both national and state effluent standards are enforced through the NPDES permit program. The NPDES permits thus "transform generally applicable effluent limitations and other standards ... into the obligations (including a timetable for compliance) of the individual discharger."
____________________
5. Under the Act, a pollutant falls into one of three categories. The Act defines "toxic pollutant" as follows: The term "toxic pollutant" means those pollutants, or combinations of pollutants, including disease-causing agents, which after discharge and upon exposure, ingestion, inhalation or assimilation into any organism, either directly from the environment or indirectly by ingestion through food chains, will, on the basis of information available to the Administrator, cause death, disease, behavioral abnormalities, cancer, genetic mutations, physiological malfunctions (including malfunctions in reproduction) or physical deformations, in such organisms or their offspring. Id. § 1362(13). "Conventional pollutants" include, but are not limited to, "pollutants classified [by EPA] as biological oxygen demanding, suspended solids, fecal coliform, and pH." Id. § 1314(a)(4). "Nonconventional pollutants" are those which are neither toxic nor conventional.
6. A "new source" is "any source, the construction of which is commenced after the publication of proposed regulations prescribing a standard of performance under this section which will be applicable to such source, if such standard is thereafter promulgated in accordance with this section." Id. § 1316(a)(2). All other sources are "existing sources."
7. Toxic pollutants are subject to health-based effluent standards in addition to the technologybased effluent limitations discussed in the text. Id. § 1317(a). In other words, limits on toxic pollutants may be based not only on how much reduction advanced technology can achieve; they may be further limited based on health considerations.
EPA v. California ex rel. State Water Resources Control Board,
426 U.S. 200, 205, 96 S.Ct. 2022, 2025, 48 L.Ed.2d 578 (1976). All dischargers are required to obtain a permit, which is issued after public notice and an opportunity for public hearing. 33 U.S.C. § 1342(a)(l), (b)(3).
Permits are issued only so long as the point source meets all applicable effluent limitations. Id. § 1342(a)(l). If no national standards have been promulgated for a particular category of point sources, the permit writer is authorized to use, on a case-by-case basis, "best professional judgment" to impose "such conditions as the permit writer determines are necessary to carry out the provisions of [the Clean Water Act.]" Id. Thus, compliance with a permit is generally deemed to constitute compliance with the Act's requirements. Id. § 1342(k).
The effluent limitations set forth in an NPDES permit are ordinarily drafted in terms of limitations on the amount, rate, or concentration of a specific pollutant. Permits may also include limitations on key generic parameters, such as pH or biochemical oxygen demand (BOD). Footnote 8
generally include other provisions, such as monitoring and reporting requirements, compliance schedules, and management practices. See id. §§ 1314, 1318,1342(a)(2).
II As should now be evident, the comprehensive NPDES regulations are pivotal to implementation of the Clean Water Act's permit scheme. They include the full panoply of procedural and substantive requirements, including elaborations upon the statutory definitions, state program requirements, conditions to be incorporated into NPDES permits, and procedural requirements for revising or challenging a permit. It is to various portions of these final NPDES regulations that the present challenges are directed.
It is well established that the judiciary's standard of review over such agency regulations is deferential. A "presumption of regularity" extends to agency rulemakings. Motor Vehicle Manufacturers Association v. State Farm Mutual Automobile Insurance Co.,
463 U.S. 29, 43 n. 9, 103 S.Ct. 2856, 2866 n. 9, 77 L.Ed.2d 443 (1983). Under the standard of review laid down by Congress, such regulations may be set aside only if they are arbitrary or capricious, unsupported by the record, outside the scope of authority delegated to the agency by the operative statute, or not in accordance with law. 5 U.S.C. § 706(2)(A) (1982). As elaborated by the case law, an agency rule is arbitrary and capricious if the agency relies upon improper factors, ignores important arguments or evidence, fails to articulate a reasoned basis for the rule, or produces an explanation that is "so implausible that it could not be ascribed to a difference in view or the product of agency expertise." State Farm, 463 U.S. at 43, Permits 103 S.Ct. at 2867.
We are also mindful that EPA is in various respects construing the statute it is charged with enforcing. In such cases, we are to look to the statute and, if necessary, legislative history to divine the intent of Congress, which of course binds both agency and court. If Congress has not spoken to the "precise question at issue," that is, if Congress' intent on the issue at hand is unclear, then the agency's interpretation must be sustained if it is reasonable in light of the language, legislative history, and policies of the statute. Chevron
____________________
8. Generic parameters are measurements which describe a solution or aquatic environment rather than indicate the precise level of a specific chemical component or pollutant in it. The pH of a solution is a measure of its acidity or alkalinity. Biochemical oxygen demand (BOD) measures the biological or bacteriological pollution of the water. BOD is the amount of dissolved oxygen required by microorganisms in the water. It is used as an indicator of the concentration of organic matter in the water. e.g. sewage, upon which the microorganisms thrive. Unpolluted water normally is saturated with dissolved oxygen. As the concentration of organic matter increases, however, the growth of microorganisms increases the rate at which the organic matter is oxidized, thus increasing the demand for oxygen. When the oxygen is consumed more rapidly than it can be replenished from the air above the water surface, aerobic organisms and normal aquatic life die.
U.S.A. Inc. v. NRDC,
467 U.S. 837, 842-45, 104 S.Ct. 2778, 2781-83, 81 L.Ed.2d 694 (1984); see also United States v. Riverside Bayview Homes, Inc.,
474 U.S. 121, 106 S.Ct. 455, 461, 88 L.Ed.2d 419 (1985); Chemical Manufacturers Association v. NRDC,
470 U.S. 116, 105 S.Ct. 1102, 1108, 84 L.Ed.2d 90 (1985); I.N.S. v. CardozaFonseca,' U.S. -------, 107 S.Ct. 1207, 1221-22, 94 L.Ed.2d 434 (1987).
We are, as to some aspects of this case, confronted with EPA's modifications of positions previously advanced by the agency and incorporated in the Settlement Agreement. An agency's change of course with respect to a particular policy does not in itself suggest a lack of reasoned decisionmaking. To the contrary, an agency volte face may evidence careful and thorough evaluation of the policy at issue. Analogously, the agency may promulgate a final rule that differs from the proposed rule, without triggering a new round of public commentary, if the changes represent a "logical outgrowth" of the prior notice and comments. American Paper Institute v. EPA, 660 F.2d 954, 959 n. 13 (4th Cir.1981); International Harvester Co. v. Ruckelshaus,
478 F.2d 615, 632 n. 51 (D.C.Cir.1973). We should also observe that a final rule which declines to embrace a proposed policy change and stays the course with the agency's original approach can be "positive evidence of careful decisionmaking." Small Refiner Lead PhaseDown Task Force v. EPA,
705 F.2d 506, 527 (D.C.Cir.1983). The ultimate issue is, of course, whether the agency engaged in reasoned decisionmaking. With these general principles in mind, we turn to the specific challenges addressed in this opinion.
Ill The Natural Resources Defense Council contends that the regulatory definition of "new source," 40 C.F.R. § 122.2 (1985), Footnote 9 is inconsistent with the language, legislative history, and policies of the Clean Water Act. As we noted earlier, "new sources" are subject to special treatment under the Act. Section 306 of the Act provides for "new source performance standards," which are generally more stringent than standards for existing sources. 33 U.S.C. § 1316 (1982). See 49 Fed.Reg. at 38,043. Additionally, new sources are ineligible for variances from performance standards; variances are, on the other hand, potentially available to existing sources. See E.I. Dupont deNemours & Co. v. Train,
430 U.S. 112, 138, 97 S.Ct. 965, 980, 51 L.Ed.2d 204 (1977). Finally, in contrast to existing sources, NPDES permits for new sources are considered "major Federal actions" subject to NEPA's requirements, 33 U.S.C. § 1371(c)(l). "New source" is defined by section 306 as "any source, the construction of which is commenced after the publication of proposed [new source performance standards] which will be applicable to that source, if such standard is thereafter promulgated in accordance with this section." 33 U.S.C. § 1316(a)(2) (emphasis added). Section 306 expressly requires that final regulations be promulgated within 120 days after publication of proposed regulations. Id. § 1316(b)(l)(B). Relying upon this latter provision, EPA in the regulation now challenged by NRDC defines "new source" as a facility on which construction commences after the proposal of applicable new source performance standards "but only if the standards are promulgated in accordance with section 306 within 120 days of their proposal." 40 C.F.R. § 122.2. See supra note 6. Unconvinced by EPA's approach in tracking the statutory lan-
____________________
9. 40 C.F.R. § 122.2 (1985) defines "new source" as follows: New source means any building, structure, facility, or installation from which there is or may be a "discharge of pollutants," the construction of which commenced: (a) After promulgation of standards of performance under section 306 of CWA which are applicable to such source, or (b) After proposal of standards of performance in accordance with section 306 of CWA which are applicable to such source, but only if the standards are promulgated in accordance with section 306 within 120 days of their proposal.
guage itself, NRDC argues that the Clean Water Act mandates application of new source performance standards to all facilities commenced after publication of proposed regulations, regardless of when the regulations are issued in final form.
The obvious difficulty of NRDC's interpretation is that it rests upon one portion of the statutory definition and ignores the remaining part. To read out of a statutory provision a clause setting forth a specific condition or trigger to the provision's applicability is, we should have thought, an entirely unacceptable method of construing statutes. 2A Sutherland, Statutes and Statutory Construction §§ 46.05, .06 (C. Sands rev. 4th ed. 1984). If there were any doubt that statutes must be read as a whole, and we cannot fathom how there would be, we will reaffirm that settled method of reading statutes. See, e.g., National Soft Drink Association v. Block,
721 F.2d 1348, 1352 (D.C.Cir.1983); National Insulation Transportation Committee v. ICC,
683 F.2d 533, 537 (D.C.Cir. 1982); Greyhound Corp. v. ICC,
668 F.2d 1354, 1362 (B.C.Cir.1981). See generally Frankfurter, Some Reflections on the Reading of the Statutes, 47 Colum L.Rev. 527, 533, 538 (1947).
NRDC's interpretation, while simplifying the statute, has the admitted and untoward effect of blue penciling out express conditional language in the statute. That language clearly seems intended to have "restrictive significance." See Reiter v. Sonotone Corp.,
442 U.S. 330, 339, 99 S.Ct. 2326, 2331, 60 L.Ed.2d 931 (1979). It would be illegitimate for the judiciary, in pursuit of some overriding Congressional goal (such as eliminating water pollution), to tear asunder a specific provision which Congress saw fit to enact. It scarcely needs repeating that statutes are rarely, if ever, unidimensionally directed towards achieving or vindicating a single public policy. See Board of Governors v. Dimension Financial Corp.,
474 U.S. 361, 106 S.Ct. 681, 689, 88 L.Ed.2d 691 (1986); International Brotherhood of Teamsters, et al. v. Interstate Commerce Commission,
801 F.2d 1423, 1430 (D.C.Cir.1986), pet'n for reh'g granted,
818 F.2d 87 (D.C.Cir.1987). While a broad policy goal may well be the animating force driving the legislation, achievement of actual passage of the measure invariably requires compromise and accommodation. Board of Governors, 106 S.Ct. at 689. So here in this landmark environmental statute, the pertinent definition is quite clear, encompassing facilities commenced after the publication of proposed standards if that standard is thereafter promulgated in accordance with the subsequent provision of section 306. One such requirement expressly laid down by the statute, as we have seen, is promulgation of the final regulation within 120 days of publication of the proposed regulation.
When the statute is clear in evidencing Congress' intent, there is ordinarily no warrant for resorting to legislative history. Burlington Northern Railroad Co. v. Oklahoma Tax Commission, ' U.S. ------, ----, 107 S.Ct. 1855, 1858-60, 95 L.Ed.2d 404 (1987). Repair to debates and reports and other precursors to law is ever fraught with difficulty. See, e.g., International Brotherhood of Teamsters, 801 F.2d at 1428 n. 4; Abourezk v. Reagan,
785 F.2d 1043, 1054 n. 11 (D.C.Cir.1986), cert, granted, ' U.S. --------, 107 S.Ct. 666, 93 L.Ed.2d 718 (1986); Hirschey v. FERC, 111 F.2d 1, 7-8 & n. 1 (D.C.Cir.1985) (Scalia, J., concurring). Such recourse, we believe, is much to be avoided if no ambiguity infects the language which Congress enacted and the President signed into law. Eagle-Picher Industries v. EPA,
759 F.2d 922, 929 n. 11 (D.C.Cir.1985). But even accepting the invitation to leave that upon which Congress and the President acted, Footnote 10 we find in the
____________________
10. We have recently been reminded that what seems clear on its face may in fact be infected with ambiguity. Young v. Community Nutrition Inst.,
476 U.S. 974, 106 S.Ct. 2360, 90 L.Ed.2d 959 (1986). Accordingly, we have not contented ourselves with exclusive reliance on the statute's plain meaning, even though we must confess that the statute by its terms seems abundantly clear in this respect.
history of this enactment little that is instructive in this specific regard.
The original Senate bill defined "new sources" solely in terms of the date of publication of either proposed or final standards. See S. 2770, 92d Cong., 1st Sess. § 306(a)(2) (1971), reprinted in A Legislative History of the Federal Water Pollution Control Act Amendments of 1972, at 162324 (1973) (1972 Legislative History). That provision would have vindicated NRDC's approach. But that approach was not destined for enactment. The House bill added the triggering "in accordance with" language. H.R. 11896, 92d Cong., 1st Sess. § 306(a)(2) (1972), reprinted in 1972 Legislative History at 990. The Conference Committee thereafter adopted the House's approach. As is so frequently the case, the reason for the Conference Committee's embracing the added language is nowhere revealed in the mists of legislative history. But what does seem clear is that the provision reflects Congress' accommodation of two competing policies. On the one hand, as the Third Circuit has rightly said, "Congress intended to subject as many firms as possible to the new source regulations." Pennsylvania Department of Environmental Resources v. EPA,
618 F.2d 991, 999 (3d Cir.1980). But that policy, standing alone, would argue in favor of universal coverage, treating that which is old as new. Congress did not go so far. Thus it was that the new source-existing source distinction is premised upon the policy determination that pollution controls implemented during the period of planning and construction of new plants was "the most effective and, in the long run, the least expensive approach to pollution control," S.Rep. No. 414, 92d Cong., 1st Sess. 58 (1971), U.S. Code Cong. & Admin.News 1972, pp. 3668, 3724, reprinted in 1972 Legislative History at 1476. It was this approach that was to be preferred to the high cost of retrofitting, H.R.Rep. No. 911, 92d Cong., 2d Sess. 110 (1972), reprinted in 1972 Legislative History at 797, which would be the necessary consequence of treating that which was old (or more precisely, existing) as new. This policy choice is reflected in the 120-day window; as EPA well put it, "construction of a source to meet new source performance standards can only proceed in a meaningful way if final standards are available." 44 Fed.Reg. at 32,858. The Third Circuit has aptly described the 120-day limitation as: [serving] to limit the period during which businesses contemplating construction, put on notice by a proposal for a standard, are left in a state of uncertainty with respect to final agency action. Congress said, in effect, that it is not unreasonable, once a business has been put on notice of a proposed standard affecting it, for that business to pattern its conduct for four months to the likely application of the standard. Pennsylvania Department of Environmental Resources, 618 F.2d at 999. That is to say, Congress must have concluded that a period of uncertainty extending beyond 120 days was unreasonable, that economic life had to go on, and that American industry should not have to languish in doubt as to when non-final regulations would eventually enjoy the force of law. It is well-settled that in such cases it is not for the judiciary to "substitute its own construction of a statutory provision for a reasonable interpretation made by the administrator of an agency." Chevron, 467 U.S. at 844, 104 S.Ct. at 2782. We reject NRDC's attempt to write out the clear language that Congress saw fit to enact or, assuming the existence of ambiguity even where clarity nonetheless appears to us, see supra note 10, to overturn a reasonable agency interpretation of the statute. Footnote 11
____________________
11. In so holding, we respectfully disagree with the Third Circuit's approach both in this statutory arena and its decision which remanded similar "new source" definitions in the coal mine and general pretreatment regulations. See National Ass'n of Metal Finishers v. EPA,
719 F.2d 624 (3d Cir.1983), rev'd on other grounds sub notn. Chemical Manufacturers Ass'n v. NRDC,
470 U.S. 116, 105 S.Ct. 1102, 84 L.Ed.2d 90 (1985); see also Pennsylvania Dep't of Environmental Resources v. EPA,
618 F.2d 991 (3d Cir.1980). In Pennsylvania Dep't of Environmental Resources, our sister circuit concluded that the only interpretation of section 306 consistent with the Clean Water Act's policy of maximizing the number of businesses subject to
IV In enacting section 306 of the Clean Water Act, Congress intended to subject new sources to the most stringent regime of technology-based standards. In exchange for this exacting approach, Congress added a provision which provided new sources a measure of protection against early, legally mandated obsolescence of their investments in pollution control equipment. Specifically, section 306(d) of the Act grants a qualifying "new source" a ten-year period of exemption from any "standard of performance" more stringent than the standard to which it was subject at the time of construction. 33 U.S.C. § 1316(d).
NRDC challenges EPA's interpretation of "more stringent standard of performance." The reason for NRDC's disagreement is that EPA's interpretation is not limited to new source performance standards (NSPS), but rather provides the ten3?ear grace period from other more stringent technology-based standards as well, such as BAT, BPT (best practicable control technology), and BCT. Footnote 12
Section 306(d) provides: Notwithstanding any other provision of this chapter, any point source the construction of which is commenced after October 18, 1972, and which is so constructed as to meet all applicable standards of performance shall not be subject to any more stringent standard of performance during a ten-year period beginH5 ning on the date of completion of such construction or during the period of depreciation or amortization of such facility whichever period ends first. 33 U.S.C. § 1316(d). Since this provision applies only to "new sources," the "applicable standards of performance" which must be satisfied to qualify for the grace period are clearly NSPS standards, as those are the standards applicable to new sources. Moreover, the term "standard of performance" in this provision is defined in a prior subsection, section 306(a)(l), to mean NSPS standards. Id. § 1316(a)(l). If this specific definition is indeed incorporated into the grace-period provision, then the literal reading of section 306(d), championed by NRDC, would grant new sources ten years of protection only against more stringent NSPS standards. There is an obvious drawback in embracing this fundamentalist approach to construing section 306(d). It would render utterly meaningless the grace period created by the statute. By definition, NSPS standards apply only to "new sources," that is sources built after an NSPS standard is proposed. Id, § 1316(a){2). (This assumes, of course, final promulgation within the requisite 120 days.) NSPS standards never apply to existing sources, as we discussed at some length in the preceding section of this opinion. Once a new source, subject to the applicable NSPS standards, becomes an existing source, subsequently promulgated NSPS standards
____________________
the new source standards was that advanced here by NRDC. 61S F.2d at 999-1000. We are persuaded, however, that that policy is but one of several underlying section 306, see id. at 999. While EPA's incorporation of the 120-day limit into the "new source" definition is arguably less than the optimal resolution of these policies, it is nevertheless at minimum a reasonable construction of the statute. We can ask no more. Chevron, 467 U.S. at 842-45, 104 S.Ct. at 278183.
12. The Act imposes a two-phase pollution control scheme for existing industrial sources which requires the attainment of progressively more stringent standards by established deadlines. By 1977, existing sources were required to achieve effluent limitations reflecting the application of the "best practicable control technology" (BPT). This standard generally reflected the "average performance of the best existing plants." Tanners' Council, Inc. v. Train, 540 F.2d 1188, 1191 (4th Cir.1976); American Meat Inst. v. EPA,
526 F.2d 442, 453 (7th Cir. 1975). By 1984, existing sources were to satisfy a more demanding standard of the "best available technology economically achievable" (BAT), which reflected the greatest attainable level of effluent reduction which could be achieved. In determining this standard, EPA could consider even plant processes or control technologies "that have not been applied as long as the record demonstrates that there is a reasonable basis to believe that the technology will be available by 1983." Tanners' Council of America, 540 F.2d at 1195. Achievement was required by 1984 of effluent limitations for "conventional" pollutants which reflect the "best conventional pollution control technology."
cannot by law apply to that facility. While it stands to reason that NSPS standards will periodically be revised, the newest NSPS standards can only be applied to subsequently built sources (or, again, to those constructed within the 120-day period after the proposed regulations are published if they are finally promulgated within that period).
Our task, as always, is to divine Congress' intent, mindful that to adopt NRDC's approach would, in effect, write the grace period out of the law. It is to that inquiry that we now turn'what did Congress intend in crafting the ten-year grace period? First of all, it seems evident that Congress enacted an entire subsection of section 306 in order to create a ten-year period of protection against something. Congress was attempting to craft a provision providing new sources with predictability both as to the expected useful life of their pollution-control facilities and as to the standards those facilities would be required to meet. See H.R, Rep. 911, 92d Cong., 2d Sess. 103-04 (1972), reprinted in 1972 Legislative History at 790-91.
Describing this issue of statutory construction as a "vexing legal problem" which has concerned EPA since 1972, 44 Fed.Reg. at 32,872, the agency sought to give meaning to the grace-period provision by interpreting "standard of performance" to mean not only new source performance standards but all technology-based performance standards created by section 301, that is, BAT, BPT, and BCT. 40 C.F.R. § 122.29(d)(l). A modicum of textual basis for this interpretation is found in the opening clause of section 306(d), "Notwithstanding any other provision of this chapter," 33 U.S.C. § 1316(d) (emphasis added). The "chapter," it bears emphasis, refers to the entire Clean Water Act. This clause could thus be taken to suggest that the grace period is to be provided despite any inconsistencies or conflicts with other provisions of the Act, which would seemingly, if somewhat oddly, include the definition of "standard of performance." This exclusionary language also indicates that the grace period could have worked an exception to the entire Act, once the new source meets the high statutory standard of "all applicable standards of performance." But EPA did not go so far as to exempt new sources from all such requirements. Specifically, the agency did not extend the protection period beyond technology-based performance standards to encompass water quality-based standards. See 40 C.F.R. § 122.29(d)(2)(i). EPA stopped short of that full measure of protection for two reasons. First, the term "standard of performance" is a term of art referring to technology-based standards. Footnote 13
Second, an earlier, unenacted version of this provision granted a grace period from both technology-based and water quality-based standards. H.R. 11896, 92d Cong., 2d Sess. § 301(f) (1971), reprinted in 1972 Legislative History at 965-66 (exempting the facility from "any more stringent effluent limitations"). Footnote 14
The narrower language of the statute as enacted suggests an intent to limit the protection provided by the grace period to technology-based standards.
B In addition, EPA declined to construe "standard of performance" to include all technology-based standards, including


