Opinion ID: 346619
Heading Depth: 1
Heading Rank: 3

Heading: Permit Conditions

Text: 62
63 The limitations on the six chemicals, ammonia, cyanide, phenol, chloride, sulphate and fluoride, and the thermal limitations are, as we have seen, state limitations adopted by Indiana pursuant to its plenary power preserved by § 510. They were included in the permit because § 402(a)(1) required the Administrator to condition the discharge permit on compliance with all applicable requirements of, inter alia, § 301, and § 301(b)(1)(C) requires dischargers to achieve, in addition to the technology-based effluent limitations determined by EPA, any more stringent limitation, including those necessary to meet water quality standards . . . established pursuant to any State law or regulation (under authority preserved by Section 510) . . . . 64 (1) Chemical Limitations 65 The limitations for the six chemicals are aggregate weight limits on the total discharges that may be made from all the outfalls at which those chemicals are discharged, which are the river outfalls. The allowable discharges are not allocated among the individual outfalls. 19 Compliance, however, is determined by monitoring at each outfall. 66 In challenging these limitations, U.S. Steel argues that the water quality standards on which certain limitations are based are invalid. As we have held in Parts III, A(4) and III, B(1), supra, however, those standards are not subject to review in either of the appeals presently before us. The company also argues that the limitations on the six chemicals are impossible to achieve with present technology. Even if this is true, 20 it does not follow that they are invalid. It is clear from §§ 301 and 510 of the Act, and the legislative history, that the states are free to force technology. 21 Although the Indiana Board considered technology in setting some of these limitations, it was not required to do so. Only the federal effluent limitations must be technology-based, and they represent the minimum level of pollution reduction required by the Act. See Leg. Hist., at 1468. If the states wish to achieve better water quality, they may, even at the cost of economic and social dislocations caused by plant closings. See Leg. Hist., at 231, 1282. Cf. Union Electric Co. v. EPA, 427 U.S. 246, 96 S.Ct. 2518, 49 L.Ed.2d 474 (1976). Thus we reject this argument as well. 67 U.S. Steel also asserts in conclusory terms that the limitations on the six chemicals are not based upon substantial evidence and are arbitrary. If this is intended as an argument that the allocations are more stringent than would be necessary to achieve the water quality standards, it fails for two reasons: 68 First, notwithstanding EPA's overgenerous concession to the contrary, 22 this necessity argument is not available in this proceeding. Section 301(b)(1) (C), the ultimate source of the Administrator's obligation to put the state limitations in the permit, is not limited to restrictions based on water quality standards but extends to any more stringent limitation the state adopts pursuant to the authority preserved by § 510. As we read the Act, the Administrator had no more authority to inquire into whether the limitations adopted by the state were necessary to achieve the water quality standards than he did to inquire into the validity of those standards. 69 Second, even if a necessity argument could be entertained in this proceeding, U.S. Steel has presented its objections in such a general and conclusory way that we doubt such an argument was intended. Assertions that the limitations are not based upon substantial evidence and not supported by accurate data and analysis and sound scientific principles, without elaboration or discussion of the information in the record which is pertinent to each limitation, cannot be considered. 23 Ours is an adversary, not an inquisitorial, system. Neither time nor expertise is available to us for searching a voluminous record for error in response to such general assertions as these. The fact that the entire record has not even been brought before us, 24 and we therefore could not exclude the possibility of record support for a given limitation in data which were not made available, leads us to believe that these arguments were included in the brief as rhetoric rather than as a serious challenge to the record support for each limitation. 25 70 We accordingly overrule the objections to the limitations on the six chemicals. 71 (2) Thermal Limitations 72 The permit also establishes limitations, effective July 1, 1977, on the temperature of the adjacent receiving waters of Lake Michigan and the Grand Calumet River after admixture of the discharges. 26 Monitoring requirements of the permit enable EPA to measure U.S. Steel's compliance with the thermal limitations. The limits are taken directly from the Indiana water quality standards applicable to the two bodies of water. The permit offers U.S. Steel an alternative to compliance with these limitations as authorized by § 316(a) of the Act. Under that section, the company may attempt to 73 demonstrate to the satisfaction of the Administrator . . . that (the) effluent limitation(s) proposed for the control of the thermal component of (its) discharge . . . (are) more stringent than necessary to assure the projection (sic ) and propagation of a balanced, indigenous population of shellfish, fish, and wildlife in and on (Lake Michigan and/or the Grand Calumet River). 74 If the company's showing is successful, EPA may set less stringent thermal limitations, provided they still meet the aquatic-life requirements. U.S. Steel challenges both the thermal limitations and the thermal demonstration provisions of the permit. 75 U.S. Steel argues that the thermal limitations in this permit are vague, arbitrary and unreasonable. As effluent limitations based directly on state water quality standards 27 and included in the permit pursuant to § 301(b) (1)(C), however, the thermal limitations are not open to substantive challenge in this proceeding. The company's related claim that compliance with the limits cannot be reliably determined must be rejected insofar as it is an objection to the permit's use of temperature as the measurement scale for determining compliance with thermal water quality standards. 28 We know of no alternative measurement scale. And, although thermal monitoring is necessarily imprecise, it is possible to determine whether a discharger is in substantial compliance with thermal effluent limitations. The thermal limitations in the permit are therefore upheld. 29 76 U.S. Steel also objects to the thermal discharge demonstration provision of the permit, included pursuant to § 316(a), which offers the company an opportunity to demonstrate that the thermal limitations imposed by the permit are more stringent than necessary to protect aquatic life. First, U.S. Steel argues that it is unfair to make such a demonstration the sole method by which a permittee can obtain relief from improper thermal limitations, (especially) . . . where the permittee is attacking the validity of the thermal limitations themselves. We have held, however, that U.S. Steel cannot challenge the validity of the thermal limitations in this proceeding. The fairness argument must be addressed to the Congress, not this court. 77 Second, the company argues that the permit improperly applied § 316(a) and its implementing regulations, 40 C.F.R. part 122. See Appalachian Power Co. v. Train, supra, 545 F.2d at 1371-1372. The argument that the Grand Calumet River would not exist, much less contain a balanced aquatic life, without U.S. Steel's discharges from Gary Works goes to the validity of the thermal limitations themselves, and is therefore not available in this proceeding. The argument that the study requirements are too vague to enable the company to comply with them does not persuade us. Accordingly, the thermal discharge demonstration provision is upheld. 30 B. Technology-Based Effluent Limitations 78 (1) At All Outfalls Except # 017 79 U.S. Steel attacks all the effluent limitations indiscriminately as arbitrary and unsupported by substantial evidence. Its broadside argument, if read literally, is that no limitation for any outfall is supported by substantial evidence and all are arbitrary. It should first be noted that an examination of the Regional Administrator's decision shows that U.S. Steel did not object before the agency to many of the limitations. Moreover, U.S. Steel's brief does not particularize its claim with respect to any outfall or limitation. As we said in considering the challenge to the limitations on discharges of the six chemicals, a court will not, in response to such a general assertion of error, sift a vast administrative record, only a portion of which has even been brought before it by the parties, for evidence arguably bearing on each limitation. In view of U.S. Steel's failure to particularize, it is not surprising that EPA's brief does not address itself to individual limitations. This means, however, that we have no guidance from either side in analyzing the evidence relating to particular limitations. 80 We would forfeit the benefits of the adversary system if we undertook the independent and unassisted search for error which would be necessary to determine the accuracy of U.S. Steel's general assertion of arbitrariness and lack of record support. This court will consider a challenge to an effluent limitation in an NPDES permit only if our attention is directed by the petitioner's brief to the specific limitation and the alleged deficiencies in the supporting evidence or reasoning of the agency. 31 81 (a) Statistical Analysis 82 As we noted above, EPA and U.S. Steel agree that BPT is currently in place at all outfalls but # 017 (which is discussed separately below). The company argues that technology-based limitations on those outfalls should be no more stringent than past operating levels, but EPA contends that in certain instances past operations do not reflect the careful and efficient operations required under the NPDES permit program. The past operating levels are reflected in the monitoring data included in the monthly reports submitted by U.S. Steel to the Indiana Stream Pollution Control Board from 1973 to 1975. 32 EPA's engineers used these data in calculating the permit limitations, but they disregarded extremely high discharge values they considered unrepresentative of proper plant or treatment-facility operations. U.S. Steel argues that this method was in error. Its proposed limitations were based on a statistical analysis of all the monitoring data, including the aberrations, and were computed so as to predict with a specified degree of accuracy, such as 95 percent, that no more than a given percentage of samples, such as 5 percent, would exceed the limitations. 83 U.S. Steel points out that EPA discarded the high values without actual knowledge of their causes, although EPA witness Spyropoulos, a former design engineer for U.S. Steel who participated in EPA's development of the effluent limitations, testified to a number of possible causes. He and the other EPA witnesses agreed with U.S. Steel that statistical analysis was one appropriate method for computing effluent limitations, and so do we. We also agree with EPA, however, that it is entitled to use its expertise in pollution-control technology in judging the reliability or representative quality of particular data. See American Meat Institute v. EPA, 526 F.2d 442, 457 (7th Cir. 1975); FMC Corp. v. Train, 539 F.2d 973, 986 (4th Cir. 1976). Although EPA did not determine the specific cause of particular high values, our review of all the monitoring data persuades us that its decision to exclude those values as aberrations was a permissible one. As EPA exhibits demonstrate, the Gary Works regularly operated at discharge levels well below those indicated by the excluded values during the 29-month monitoring period. The range among the values used in EPA's calculations illustrates the operating flexibility available to U.S. Steel under the EPA method. 84 There are two additional reasons for rejecting the U. S. Steel proposal. First, we agree with the testimony of the EPA witnesses that one of the goals of the NPDES permit program is to insure that pollution-control facilities are operated as efficiently and carefully as possible. The U. S. Steel proposal, with effluent limitations derived from data taken before the permit was issued, may build in a factor for human or mechanical lapses that should not be tolerated. 85 Second, the limits proposed by U. S. Steel would, as EPA observes in its brief, actually allow an increase in the discharge of pollutants from Gary Works. 33 U. S. Steel attempts to justify this result by showing that its proposal was consistent with EPA's own guidelines for the steel industry. The company derived its proposed daily maximum limits by multiplying the daily average limits by three, in accord with those guidelines. See 40 C.F.R. part 420 and 39 Fed. Reg. 24118 (change # 6) (June 28, 1974). It failed however, to demonstrate that EPA intended the factor of three as anything but a rough approximation of the daily fluctuations likely to occur in the steel-manufacturing process. Where, as here, the performance data show the plant to be capable of operating on a regular basis within a relatively narrow range far below the arbitrary multiplier of the guidelines, EPA may use the power granted it by § 402(a)(1) of the Act to set limitations lower than those that would result from use of the arbitrary multiplier. See Leg. Hist., at 170, 176, 1468. To do otherwise would be to authorize an increase in the pollutants discharged by the plant, a result Congress certainly did not intend. See note 44, infra. 86 (b) Surface-Runoff Effects 87 U. S. Steel next argues that, if the more lenient effluent limitations it proposes are not accepted, then at least monitoring samples taken during periods of surface runoff resulting from rainfall or melting snow should be disregarded in determining compliance with the NPDES permit. 88 As is demonstrated by the testimony of EPA witness McDermott, also an EPA engineer formerly employed by U. S. Steel, the agency considered surface-runoff effects in developing the effluent limitations for Gary Works. EPA's analysis revealed that the surface runoff from a day-long storm of .4 inches per hour, over the entire drainage area of Gary Works, would comprise only slightly over 10 percent of the plant's total water discharges for that day. The process-water portion of this total volume would be treated. 34 The portion of the runoff that found its way into the 12 primarily cooling-water outfalls would have little or no ground contact because of the roof drains or, in the case of the runoff from the yard and road drains, would be taken to a sewer for treatment. And, if surface runoff did increase the concentration of total suspended solids in the cooling-water discharges, it would presumably increase those concentrations in the intake as well. The permit provision allowing U. S. Steel to calculate TSS levels on a net basis thus obviates to a great extent the need for a special surface-runoff exception. 89 Finally, we note that U. S. Steel itself offered no proof of the extent of this supposed surface-runoff effect on the Gary Works. The rainfall data that were presented were based on conditions at Midway Airport in Chicago, and even this information was not correlated with particular high discharge values revealed by the data from the 29 months of monitoring. Thus we are unable to determine what effect surface runoffs have had on the discharge levels or the treatment facilities at the Gary Works. 90 Accordingly, EPA was not required to accept U. S. Steel's contention that exemptions should be granted for surface runoffs. 91 (2) Outfall # 017 92 (a) BPT and Variance 93 Before the issuance of the October 1974 permit in this case, EPA promulgated single-number effluent guidelines and limitations for the iron and steel manufacturing point-source category. 39 Fed. Reg. 24114 (June 28, 1974); 40 C.F.R. part 420. 35 In U. S. Steel's permit the TSS limitations for outfall # 017, which serves the iron-making blast furnaces, were calculated from these limitations, 40 C.F.R. § 420.42, which, as is apparent from the Development Document, were based on EPA's conclusion that recycling constituted BPT for iron-making blast furnaces. Cf. E. I. duPont de Nemours & Co. v. Train, 430 U.S. 112, 122, 132 n. 23, 97 S.Ct. 965, 972, 977 n. 23, 51 L.Ed.2d 204 (1977). 94 In American Iron & Steel Institute v. EPA, 526 F.2d 1027 (3d Cir. 1975) (AISI (I) ), the steel industry challenged various aspects of the regulations, but did not attack the 1977 TSS limitations based on the conclusion that recycling was BPT. The Third Circuit, while remanding the 1977 regulations, explicitly upheld the new-source and 1983 limitations on TSS discharges from iron-making blast furnaces, thereby approving recycling-based limitations twice as stringent as the 1977 limitations. The court's remand was based in large part on its conclusion that § 301 limitations must specify a range of effluent reductions attainable through the application of BPT rather than single numbers. Apart from the fact that the Supreme Court's approval of single-number effluent limitations in duPont renders this conclusion questionable, even the Third Circuit's remand dealt only with the agency's § 304(b)(1)(A) calculation of the degree of effluent reduction attainable by installing blast-furnace recycling; the underlying § 304(b)(1)(B) determination that recycling constitutes BPT remained unaffected. Thus, whether or not the entire iron and steel guidelines and limitations are resurrected by the duPont decision, the treatment in AISI (I) of the TSS limitations for iron-making blast furnaces leaves unimpeached EPA's conclusion that recycling is BPT. 95 Nevertheless, following that decision, the EPA Regional Administrator ordered a limited remand of the instant permit proceeding, in order to develop further data on the best practicable engineering judgment as to what constitutes bpt for the iron-making blast furnaces at Gary Works. After the remand, new TSS limits were developed for outfall # 017 based on EPA's determination that a blast-furnace recycling system constitutes the best practicable control technology currently available for that phase of the iron-making process, § 304(b)(1)(B). 96 U. S. Steel challenges EPA's determination that blast-furnace recycling constitutes BPT for the iron-making process at the Gary Works on three grounds: (1) EPA failed to consider the six factors set forth in § 304(b)(1)(B) as relating to the assessment of (BPT), and therefore the agency's designation of recycling as BPT was improper. (2) Installation of a recycling system would cause violations of the sulphate limits in the permit, and therefore recycling is not a practicable technology for Gary Works. (3) A recycling system cannot be built and placed in operation at Gary Works before July 1, 1977, and therefore is not currently available to U. S. Steel. 36 97 To begin with, we believe it was unnecessary for EPA to reexamine the BPT question following the remand in AISI (I). As duPont makes clear, technology-based § 301 effluent limitations and § 304 guidelines, and necessarily the BPT on which they are based, are uniform national standards and are not to vary from plant to plant. duPont v. Train, supra, 430 U.S. at 127, 130-132, 136-137, 97 S.Ct. at 974, 976, 979; see also AISI v. EPA, supra, 526 F.2d at 1043. When no limitations or guidelines are yet available, NPDES permits are to be issued under § 402(a)(1) upon such conditions as the Administrator determines are necessary to carry out the provisions of this Act. See Natural Resources Defense Council, Inc. v. Train,166 U.S.App.D.C. 312, 510 F.2d 692, 709-710 (1975). We believe that under these circumstances the BPT to be ascertained by EPA is still a uniform national standard for the class or category of plants of which the plant in question is a member. Therefore, even if the applicable BPT had not already been determined, the appropriate inquiry for EPA would have been, not what constituted BPT for the Gary Works, but what constituted BPT for the category and class of point sources of which the Gary Works was a member. In fact, however, EPA had already determined BPT for iron-making blast furnaces in developing the limitations which were remanded in AISI (I). This BPT determination, and the nationally uniform TSS limitations based thereon, unimpeached, as we have seen, by the AISI (I) remand, constitutes a proper basis for establishing the TSS limitations in the permit for the Gary Works. It was unnecessary for EPA to consider the § 304(b)(1)(B) factors anew in this proceeding or otherwise reexamine the BPT issue. 98 The proper inquiry for EPA, in establishing the permit limitations in this proceeding, was whether the circumstances of the individual plant warranted a variance from the nationally uniform limitations. Although the Act itself provides for individual source variances only from the 1983 limitations, 37 the Supreme Court's opinion in duPont v. Train, supra,430 U.S. at 127-128, 97 S.Ct. at 975, infers variance authority in EPA with respect to the 1977 limitations as well. EPA has regularly included variance provisions, allowing different effluent limitations if fundamentally different factors are shown, in its regulations containing 1977 limitations, and it did so in the iron and steel regulations remanded in AISI (I). 38 99 The agency's reexamination of the BPT issue as if it were obligated to determine BPT for the Gary Works individually was the equivalent of determining whether there were fundamentally different factors at that plant which made BPT impracticable there and thus justified a variance from nationally applicable limitations based on BPT. From EPA's conclusion that recycling was BPT for the Gary Works it follows that the plant was not entitled to a variance. We now examine the facts and reasoning underlying that conclusion. 100 In both the initial hearing and the hearing on remand EPA considered the Development Document and other information it had used in formulating the guidelines and limitations for the iron and steel industry. 39 At the hearing on remand two EPA employees, James McDermott and Peter Spyropoulos, testified concerning the applicability of recycling technology to the Gary Works. The record demonstrates that EPA analyzed the § 304(b) factors with respect to the Gary Works specifically, as well as with respect to the steel industry in general. Furthermore, substantial evidence supports EPA's designation of blast-furnace recycling as BPT for the iron-making process in the steel industry generally and the reasonableness of imposing limitations on the Gary Works based on that BPT. 101 It is undisputed that recycling significantly reduces TSS levels in water discharged from iron-making blast furnaces. Moreover, as McDermott testified, the reduction in water flow achieved by the recycling system also increases the concentration of other pollutants, thereby rendering them susceptible to treatment or disposal which would otherwise be impossible or uneconomic. 40 102 The Development Document notes that although a majority of the (steel) plants around the country are operating on a once-through basis, recycling is employed as a water conservation device in many plants. Spyropoulos testified that he helped design a recycling system similar to the one EPA proposes here; that system was installed at U. S. Steel's own South Works Plant in South Chicago by December 1970. Blast-furnace recycling is already in place at nearly all the iron-making facilities in the Chicago area; it is, as noted in the Development Document, a well-established art. 41 103 Both McDermott and Spyropoulos testified that blast-furnace recycling could be installed at the Gary Works. Their testimony was based on an inspection of the plant, a survey of four different steel plants employing blast-furnace recycling, and discussions with manufacturers, contractors, and others. They also testified regarding the pollution-control facilities now in place at Gary Works, the new facilities and equipment needed for a recycling system there, and the costs and time required to construct and operate such a system. 42 104 EPA could reasonably conclude that, despite the age of the iron-making blast furnaces at Gary Works, retrofitting would be feasible. Recycling has been installed at U. S. Steel's older South Works Plant and other existing iron-making blast furnaces. Because it is a part of the post-process treatment, it does not require changes in the manufacturing process itself. EPA's conclusions demonstrate that a variance based on infeasibility of recycling for the Gary Works was not justified. Compare AISI v. EPA, supra, 526 F.2d at 1048. 105 We also reject U. S. Steel's argument that the TSS limitations based on recycling as BPT are improper because recycling would result in violations of other limitations in the permit, specifically those governing discharges of sulphate. This argument is based on the fact that the acidity-alkalinity control unit, which would be included in the proposed recycling system to minimize scaling, would use sulphuric acid to lower pH. See note 40, supra. This would increase discharges of sulphates above the levels allowed by the sulphate limitations of the permit. 43 U. S. Steel asserts that no technology is known that will enable it to solve this problem, and that therefore either the sulphate limits or the TSS limits must give way. 106 The sulphate limits were based on the Indiana waste load allocations, and were included in the permit pursuant to § 301(b)(1)(C). Although these limits restrict U. S. Steel to its present discharges, and may be below the level necessary to maintain water quality in U. S. Steel's segments of the stream, they are the waste load allocations adopted by the Indiana Stream Pollution Control Board and approved by EPA, under § 303(d) of the Act. Thus the sulphate limits are not subject to challenge in this proceeding, 44 and must be accepted by EPA and this court. 107 The sulphate limitations cannot be said to make recycling  impracticable at Gary Works, and therefore not BPT under § 301(b)(1)(A) or § 304(b). As we observed above, the latter section provides for a determination of BPT which will be the basis for guidelines and effluent limitations that will be uniform throughout the nation. duPont v. Train, supra, 430 U.S. at 129, 97 S.Ct. at 975. See also Leg. Hist., at 156, 162, 170. BPT, being nationally applicable, cannot be affected by the circumstances at a single plant. The real question, therefore, is whether the stricter Indiana standards justify a variance. 108 We believe they do not. The existence of state waste load allocations requiring limitations more stringent than the federal, technology-based limitations should not create a loophole through which compliance with the federal limitations may be evaded. Section 301(b)(1)(C) can hardly have been intended to authorize a state, by imposing limitations incompatible with BPT, to allow its industries to escape their duty to comply with nationally uniform federal limitations. An important reason for Congress' adoption of nationally applicable federal effluent limitations was to prevent individual states from attracting industry by adopting permissive water quality standards. See, e. g., Leg. Hist., at 156, 263, 574-575. Surely Congress never intended those federal limitations to be relaxed because a state adopted water quality standards and waste load allocations requiring more stringent pollution controls. See Leg. Hist., at 1461, 1468. Indeed, § 301(b)(1) provides that BPT-attainable effluent limitations and . . . any more stringent limitation . . . established pursuant to State law or regulations must be achieved by July 1, 1977. 109 Thus, we hold that the existence of more stringent state limitations is not one of the factors to be considered in determining whether an individual point source is entitled to a variance from a limitation based on BPT. This makes it unnecessary to consider EPA's alternative argument that there presently exists technology capable of achieving both the TSS and the sulphate limitations. See note 20, supra. 110 U. S. Steel challenges the limitations based on blast-furnace recycling on the additional ground that it cannot construct and place into operation a recycling system by July 1, 1977. 45 This contention must also be rejected. There was time to install a recycling system between October 31, 1974, when the permit was first issued, and July 1, 1977, according to the testimony of Spyropoulos. The Supreme Court has held, in construing the Clean Air Act, that litigation . . . (seeking a variance from national standards) . . . is carried out on the polluter's time, not the public's . . . . Train v. Natural Resources Defense Council, 421 U.S. 60, 92, 95 S.Ct. 1470, 1488, 43 L.Ed.2d 731 (1975). There is no reason not to apply that principle here. 46 Therefore U. S. Steel cannot use the delay between October 1974 and the present as an excuse for not installing a recycling system. 111 This conclusion is further supported by Congress' intent that BPT be determined on a nationwide basis, with substantially the same technology-based effluent limitations applicable to all similar point sources. Temporal feasibility of BPT installation is not included in the § 304(b) factors and should not be a ground for a variance. Consideration of that factor would emasculate the mandatory nature of the July 1, 1977 compliance deadline. See Bethlehem Steel Corp. v. Train, 544 F.2d 657 (3d Cir. 1976), cert. denied, --- U.S. ----, 97 S.Ct. 1666, 51 L.Ed.2d 369 (1977). Also, as the Third Circuit noted in Bethlehem Steel, Congress considered and rejected a provision of the House bill, 47 which would have enabled EPA to grant a hardship exception to the July 1, 1977 compliance deadline when it determines that it is not possible either physically or legally to complete the necessary construction within the statutory time limit. Although Congress' failure to enact this extension provision is not conclusive of its intent, it does offer some further confirmation of our conclusion that U. S. Steel was required to litigate on its own time. Id., 544 F.2d at 662. 48 112 (b) Interim Limitations 113 Sustaining EPA's conclusions that recycling is BPT and that Gary Works is not entitled to a variance from the limitations based on BPT, does not, however, end our inquiry. U. S. Steel also challenges EPA's § 304(b)(1)(A) calculation of the degree of effluent reduction attainable through the application of (BPT) at Gary Works, reflected in the interim TSS limitations. EPA calculated those limits by estimating the flow of water in the recycling system, the TSS concentration in the recycling flow, and the volume of water discharged from the system, or blowdown. 49 EPA then multiplied the blowdown volume, expressed in gallons of water per ton of iron cast, by TSS concentration figure, and multiplied the product by a daily iron-production figure. The daily average effluent limitation on TSS discharges was the result of these computations. 114 U. S. Steel does not question EPA's engineering analysis of the water flows or TSS concentration levels in the proposed recycling system. The company's argument is that EPA's use of a daily iron-production figure of 13,500 tons for outfall # 017 was improper. Both parties agree that the entire Gary Works produces an average of 20,000 tons of iron each day. About 6,500 tons of this total is usually cast by one blast furnace, number 13, which is a new furnace with its own recycling system that does not discharge through outfall # 017. Only the older furnaces, numbers 1-12, discharge through that outfall. The evidence also establishes that these older furnaces have produced up to 16,700 tons of iron in one day, and that furnace 13 has produced at least up to 8,700 tons in one day. The capacity of furnaces 1-12 is 19,971 tons per day; only eight of them need to be in operation for the group to cast 13,500 tons. U. S. Steel's memorandum prepared pursuant to the Regional Administrator's Order of Remand acknowledged that some of furnaces 1-12 are not operating at the present time. 115 Our review of the record persuades us that substantial evidence supports EPA's use of 13,500 tons as the average daily iron-production figure for the blast furnaces served by outfall # 017. U.S. Steel does not contend that this is not the normal production figure. Rather, it argues that, if furnace 13 were out of service or unable to produce at capacity for some reason, the production slack might be taken up by furnaces 1-12, resulting in higher water and TSS discharges from outfall # 017. The company argues, in effect, that the permit should be based, not an actual production, but on the capacity of furnaces 1-12, because one day they might be required to produce up to that figure. We reject this claim. If special circumstances, such as relining or repair, require U.S. Steel to shut down furnace 13, a modification of the permit can be sought. 50 The interim limit on the daily average TSS discharges from outfall # 017 reflects the usual operations at Gary Works. The daily maximum represents a 50 percent increase over the daily average discharge, permitting occasional increases in blowdown flows or TSS concentrations. Moreover, EPA's use of a 50 mg/liter figure, instead of the projected operating level of 36 mg/liter, in calculating the TSS concentrations in the blowdown and recycling waters resulted in limitations which give U.S. Steel a measure of operating flexibility. We uphold the interim effluent limitations on TSS discharges from outfall # 017. 116 U.S. Steel argues in its reply brief that EPA completely failed to determine limitations for other contaminants 51 when it calculated the degree of effluent reduction attainable by converting to blast-furnace recycling. As an argument raised for the first time in the reply brief, it need not be considered. American Meat Institute v. EPA, supra, 526 F.2d at 462. We observe, however, that here too U.S. Steel misses the distinction between the technology-based effluent limitations required by § 301(b)(1)(A) and the limitations based on state law required by § 301(b)(1)(C). U.S. Steel could not have benefited if EPA had first determined the effect of recycling on other pollutants: Indiana standards impose a ceiling on pollutants, which cannot be raised whatever the effect of recycling. 117 (c) Final Limitations 118 The interim limitations for TSS discharges from outfall # 017 are 1,688 pounds daily average and 2,532 pounds daily maximum. The permit's final limitations require U.S. Steel to reduce its TSS discharges to 500 pounds daily average and 750 pounds daily maximum by July 1, 1979. The Regional Administrator found that these limits can be achieved by installing a system which treats the blowdown from the recycling system, 52 and that U.S. Steel must install such a system in any event, in order to achieve the effluent limitations based on state law. Alternatively, he found that improved efficiency of operation of the recycle system could achieve these limitations. 53 U.S. Steel's challenge to this finding is the conclusory assertion that (t)he proper application of blast furnace recycle technology will not result in compliance with those final effluent limitations for suspended solids. (Emphasis in original.) The Regional Administrator's findings were based on two EPA exhibits introduced at the administrative hearing on remand. Inasmuch as these exhibits were not included in the parts of the record brought here by the parties, 54 we cannot examine them and must assume that they support the findings. 119 (3) Cooling-Water Intake Structures 120 The permit also requires U.S. Steel to conduct an intake monitoring program, as part of a study of the environmental impact of the cooling-water intakes for Gary Works, and to submit a proposal for meeting the § 316(b) requirement that 121 the location, design, construction, and capacity of cooling water intake structures reflect the best technology available for minimizing adverse environmental impact. 122 U.S. Steel objects to this condition, arguing that this requirement may not be applied to it because Congress only intended that steam-electric generating plants be required to comply with § 316(b), and that § 402(a)(1) does not allow EPA to condition NPDES permits upon compliance with § 316(b). 123 We reject these arguments. First, § 316(b) applies on its face to all technology-based effluent limitations applicable to a point source. U.S. Steel asks us to rely on an isolated remark in the legislative history to reject the plain meaning of the statute. 55 EPA, which is the agency charged with enforcing this statute, construes § 316(b) to apply to all point sources. That interpretation of the statute comports with its plain meaning, and we accept it. Second, as § 316(b) itself makes clear, these requirements are to be implemented through standards established pursuant to §§ 301 and 306. Thus § 402(a)(1) implicitly requires the Administrator to insure compliance with § 316(b) as one of the permit conditions. See also Appalachian Power Co. v. Train, supra, 545 F.2d at 1371-1372. 124 U.S. Steel's argument that, even if applicable, the permit provision is unreasonable must also be rejected. Not even a rough cost-benefit analysis is necessary as a basis for the requirement that the company conduct a study of the impact of the present cooling-water intake structures on aquatic life in Lake Michigan. Such a study, intended to assist EPA in developing § 316(b) effluent limitations, is well within the agency's § 308 authority. 56 Finally, the company's complaint regarding EPA's failure to compare the costs and benefits of the various technologies available to reduce the adverse environmental impacts of cooling-water intake structures comes too soon. No particular control methods are required by the permit, and we trust that EPA will conduct a limited cost-benefit analysis once the information on which an evaluation of the various technologies can be made becomes available. Accordingly, we affirm the cooling-water intake provision of the permit. C. Monitoring Requirements 125 U.S. Steel has two basic complaints regarding the monitoring required by the permit: it is to be done too often and at too many places. 126 The initial monitoring requirements contained in the permit correspond closely to U.S. Steel's present monitoring practices, as required by the Indiana Stream Pollution Control Board. 57 The final requirements increase the monitoring at all process-water outfalls, requiring daily monitoring for several pollutants as well as temperature and continuous monitoring for flow and pH at several outfalls. Both the remaining process-water and all cooling-water outfalls will be monitored once a week for several pollutants and once a month for others. All the monitoring requirements exceed those proposed by U.S. Steel and present levels, both in the frequency of measurement and in the number of pollutants for which measurements must be taken. 127 Section 308 of the Act grants the Administrator broad authority to require NPDES permittees to monitor at such locations (and) at such intervals as he shall prescribe, (w)henever (it is) required to carry out the objective of (the Act). Similarly, § 402 vests him with authority to prescribe conditions for (NPDES) permits . . . including conditions on data and information collection . . . . We conclude that the monitoring requirements set forth in the permit are within this broad authority. 128 EPA considered four factors in determining the monitoring requirements, and set the requirements separately for each outfall. These factors were: the nature of the discharges and their impact on the receiving stream; the variability of the discharges; the volume of water discharged; and the present monitoring practices of U.S. Steel. These factors are proper, and the record establishes that they were given appropriate weight by EPA. For example, because of the higher concentrations and greater variety of pollutants present in process water, the permit appropriately requires more frequent monitoring of process-water discharges than of cooling-water discharges. Similarly, more frequent monitoring was required at those outfalls which tended to fluctuate in the amount and quality of their discharges. 129 The monitoring requirements similar to or less stringent than those imposed in the approximately 50 other steel-plant permits issued in Region Five will not work an unjustified economic hardship on U.S. Steel. The chief difference between U.S. Steel's present monitoring practices and the initial requirements is that compliance at nine of the outfalls will be based on a 24-hour composite sample rather than the 8-hour composite sample presently prepared. The use of the 24-hour composite sample is extended to all outfalls by the final monitoring requirements. These changes will more than triple the number of samples taken. The use of a 24-hour composite sample will doubtless be more expensive than present monitoring practices, but it will present a more complete picture of the discharges from the Gary Works, reflecting fluctuations over the course of an entire day of production. At the outfalls monitored on a daily basis, it will allow an almost continuous check on the performance of the treatment facilities at Gary Works. 130 By comparison, U.S. Steel's permit proposals call for monitoring only once a week, even at the seven outfalls now sampled five times in eight days, and would replace the monitoring for several pollutants now conducted at each outfall with monitoring at the Pennsylvania Railroad Bridge, four-and-one-half miles downstream. Monitoring at each outfall enables the permittee and EPA to pinpoint the source of any discharges that exceed the plant-wide limitations on particular pollutants. Furthermore, the U.S. Steel proposal would, in effect, allow it to use the four-and-one-half mile stretch of the river as an extended treatment facility, something hardly contemplated by either the Indiana water quality standards or the FWPCA. 131 We cannot say that EPA exceeded its authority or acted unreasonably when it determined that regular and frequent monitoring at each outfall is necessary to insure prompt detection and rectification of permit violations. Therefore, we affirm the initial and final monitoring requirements set forth in the permit. D. Deep Well 132 The permit imposes effluent limitations and study and monitoring requirements on U.S. Steel's discharges of acid wastes into a deep well. 58 U.S. Steel challenges EPA's legal authority to impose these restrictions, 59 citing the language of the Act, United States v. GAF Corp., 389 F.Supp. 1379 (S.D.Tex.1975), 60 and the legislative history of the Act on which that decision is based. We reject U.S. Steel's argument. 133 The statute authorizes EPA to regulate the disposal of pollutants into deep wells, at least when the regulation is undertaken in conjunction with limitations on the permittee's discharges into surface waters. Section 402(a) (1) provides that the EPA's permit program shall be subject to the same terms, conditions, and requirements as apply to a state permit program. And EPA approval of a state's permit program, governing discharges into navigable waters, is conditional upon EPA's conclusion that the state program includes adequate authority . . . (t)o issue permits which . . . control the disposal of pollutants into wells. Section 402(b)(1)(D). Thus EPA's administration of an interim NPDES permit program concerning surface discharges includes the authority to control disposals into wells. 61 134 The general provisions and definitions of the FWPCA support this view of EPA's authority. Section 402(a)(1) empowers the Administrator to issue a permit for the discharge of any pollutant, or combination of pollutants, provided certain conditions are met. Pollutant is defined in § 502 of the Act to include chemical wastes . . . discharged into water. Section 502(6). One exception to the definition of pollutant, § 502(6)(B), provides that 135 pollutant . . . does not mean . . . (B) water, gas, or other material which is injected into a well to facilitate production of oil or gas, or water derived in association with oil or gas production and disposed of in a well . . . . 62 136 Applying the canon expressio unius est exclusio alterius to the quoted language, we conclude that the listed materials are pollutants when injected into wells under any other circumstances. U.S. Steel does not deny that its acid discharges into the deep well are chemical wastes within § 502(6). Therefore, their discharge into the deep well may properly be regulated by the permit-granting authorities pursuant to § 402(a)(3) and (b). 137 The legislative history also supports our construction of the statute. Exhibit 1, accompanying Senator Muskie's report of the conference committee on S. 2770 (the Act), 63 states as follows: 138 The Conferees intend that this provision (§ 502(6)(B)) assure that no injection or disposal occur in such a manner as to present a potential hazard to ground water quality. Leg. Hist., at 178. 139 During the House debate on the report of its conference committee, Representative Kemp stated that because 140 (f)or the first time ground waters have been given the same emphasis as surface waters . . . (the Act is) an important step forward in the protection of the underground environment . . . . 64 141 Similarly, the report on the House version of the Act notes its committee's intent that 142 the exclusion from the term 'pollutant' . . . appl(y) only to the properly executed injection of materials into wells to stimulate the primary, secondary, or subsequent production of crude oil or natural gas, and to the properly executed disposal in wells of brines derived in association with (their) production . . . . 65 143 Finally, the Senate Report which accompanied S. 2770 notes that EPA is to prepare guidelines for disposal of material in deep wells, Leg. Hist., at 1471, and explains that, while federally imposed standards for ground waters are not contemplated, state regulation under § 402 is required to protect ground waters and eliminate the use of deep well disposal as an uncontrolled alternative to toxic and pollution control. 66 Leg. Hist., at 1491. E. Schedules of Compliance 144 In addition to the specific discharge limitations discussed above, the permit includes schedules of compliance designed to insure that the effluent limitations required by the permit are achieved in a timely fashion. 67 These items are included in the permit pursuant to the Administrator's authority under §§ 301, 401, and 502(11) and (17). 145 U.S. Steel does not challenge EPA's authority to set reasonable schedules of compliance under these statutory provisions. Instead, the company argues that the schedules set in the permit are arbitrary, that EPA's delay in promulgating nationally applicable effluent guidelines entitles it to an extension of the July 1, 1977 deadline for achieving BPT-based effluent limitations, and that the statute is satisfied if the permittee, before the deadline, initiates a program which will eventually achieve compliance with the limitations. We reject these arguments, and substantially approve the schedules of compliance as they are set forth in the permit under review. 146 First, we disagree with U.S. Steel's general characterization of the schedules of compliance as arbitrary, capricious and without foundation. These schedules were established with the required levels of effluent reduction and the statutory deadlines in mind and appear to us to be on the whole reasonable. 147 U.S. Steel points out that several of the compliance dates had already passed by the time the permit was issued. We do not take these clearly unfair permit conditions as lightly as it appears the agency itself does. Regardless of whether they were due to a mere quirk of administrative procedure, as EPA asserts, the inclusion of dates which have already passed and therefore cannot be complied with is inexcusable. Fortunately, there was no prejudice to U.S. Steel from these inclusions, because EPA itself recognized that no enforcement action could be brought for non-compliance with those dates without violating due process. And, as the agency observes, § 309(a)(3) gives the Administrator discretion to issue a compliance order in lieu of bringing a civil action. 68 The presence of the invalid parts of the schedules, which have not prejudiced U.S. Steel, does not require us to invalidate the schedules in their entirety. 69 148 U.S. Steel's second argument, that EPA's delay entitles it to an extension, must be rejected in view of the mandatory nature of the deadlines contained in § 301(b). As we observed in our discussion of the company's claim that temporal infeasibility made recycling not currently available to it, the congressionally imposed deadline of July 1, 1977 is a firm one. 70 We agree with the view expressed by the Third Circuit in Bethlehem Steel Corp. v. Train, supra, 544 F.2d at 663, that it (is) not for the courts to upset that Congressional decision. As the Supreme Court noted in an analogous context, such a statutory deadline is not subject to judicial nullification. Union Electric Co. v. EPA, supra, 427 U.S. at 269, 96 S.Ct. 2518. 71 149 Under the FWPCA, EPA was required to promulgate § 304 guidelines for various industries by October 18, 1973. Sections 304(b)(1)(A) and 306. Natural Resources Defense Council, Inc. v. Train, supra, 510 F.2d at 704-705. The agency did not promulgate guidelines for the iron and steel industry, however, until compelled to do so by that decision. 39 Fed.Reg. 24114 (June 28, 1974). U.S. Steel argues that this delay in the statutory timetable either nullifies the July 1, 1977 deadline or entitles it to an extension of the time for compliance. We do not believe Congress intended such a result. U.S. Steel's permit was first issued in October 1974, well before the January 1, 1975 deadline apparently contemplated by Congress for the issuance of permits. See § 402(k); see also Natural Resources Defense Council, Inc. v. Train, supra, 510 F.2d at 706-710. Although EPA's guidelines were then in effect, BPT and the resulting effluent limitations would have been determined in the permit proceeding itself if they had not yet been promulgated. Id. at 709. Thus, it appears that the obligations imposed on an individual discharger by the permit are enforceable according to the statutory timetable whether or not they are based on previously issued guidelines. 150 U.S. Steel does not argue that the remand of the iron and steel guidelines and the resulting remand of this permit proceeding themselves justify an extension. As we have already held with respect to recycling as BPT, U.S. Steel must litigate on its own time. Cf. Train v. Natural Resources Defense Council, supra, 421 U.S. at 92, 95 S.Ct. 1470. 151 U.S. Steel's final argument is that the statute itself allows the July 1, 1977 deadline to be met simply by beginning action on a schedule of compliance which will eventually result in achieving the limitations based on BPT or state regulations. We reject this contorted reading of the statute. We recognize that the definition of effluent limitation includes schedules of compliance, § 502(11), which are themselves defined as schedules . . . of actions or operations leading to compliance with limitations imposed under the Act. Section 502(17). It is clear to us, however, that § 301(b)(1) requires point sources to achieve the effluent limitations based on BPT or state law, not merely to be in the process of achieving them, by July 1, 1977. See Bethlehem Steel Corp. v. Train, supra, 544 F.2d at 662. 72 152 Therefore we uphold the schedules of compliance set forth in the permit. We also deny U.S. Steel's recently filed motion for a stay pending appeal of the schedule of compliance contained in the permit for the installation of blast-furnace recycling at outfall # 017. 153 The District Court's decision in No. 76-1425 is Affirmed. In No. 76-1616 the Petition for Review is Denied.