Case ID: f2d_657/html/0298-01.html
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Date Created: 2024-08-24T03:29:51.129683

SIERRA CLUB, Petitioner, v. Douglas M. COSTLE, Administrator of the Environmental Protection Agency, Respondent, National Coal Association, Alabama Power Company, et al., Intervenors.
    Nos. 79-1565, 79-1719, 79-1867, 79-1874, 80-1187, 80-1201, 80-1213 and 80-1338.
    United States Court of Appeals, District of Columbia Circuit.
    Argued Sept. 22, 1980.
    Decided April 29, 1981.
    As Amended June 1, 1981.
    
      Henry V. Nickel, Washington, D.C., with whom George C. Freeman, Jr., Richmond, Va., Michael B. Barr, F. William Brownell, Washington, D.C., Louis E. Tosí and John Murtagh, Toledo, Ohio, were on the brief, for petitioners Appalachian Power Co., et al. in Nos. 79-1719 and 80-1187 and intervenor in Nos. 79-1867, 79-1874, 80-1201 and 80-1213.
    Joseph J. Brecher, Oakland, Cal., for petitioner Sierra Club, Nos. 79-1565 and 80— 1201 and intervenor in No. 79-1719.
    William Butler, Washington, D.C., with whom Larry Martin Corcoran and David J. Lennett, Washington, D.C., were on the brief, for petitioner, Environmental Defense Fund in Nos. 79-1874 and 80-1213. Robert J. Rauch also entered an appearance for Environmental Defense Fund.
    Mary E. Hackenbracht, Deputy Atty. Gen., State of California, San Francisco, Cal., was on the brief for petitioner, California Air Resources Bd. in Nos. 79-1867 and 80-1388.
    Earl Salo, Atty., Environmental Protection Agency, Charlotte Uram, Atty., Dept, of Justice, Washington, D.C., with whom Angus MacBeth, Acting Asst. Atty. Gen., Dept, of Justice and Todd M. Joseph, Deputy Associate Gen. Counsel, Environmental Protection Agency, Washington, D.C., were on the brief for respondents. James Moor-man and Mark Sussman, Attys., Dept, of Justice, Washington, D.C., also entered appearances for respondents.
    Ridgway M. Hall, Jr., Washington, D.C., with whom John A. Macleod, Timothy M. Biddle and John T. Scott, III, Washington, D.C., were on the brief for intervenor, National Coal Ass’n in No. 79-1565.
    George C. Freeman, Jr., Richmond, Va., Henry V. Nickel and Michael B. Barr, Washington, D.C., also entered appearances for intervenor, Alabama Power Co., et al. in No. 79-1565.
    
      Christopher S. Bond and Charles A. Blackmar, Jefferson City, Mo., also entered appearances for intervenor, Missouri Ass’n of Municipal Utilities in No. 79-1719.
    TABLE OF CONTENTS
    Page
    I. Introduction........................................................... 312
    A. The Challenged Standards .............................. 312
    B. The Parties ....................................................... 312
    C. Background ....................................................... 313
    D. Procedural History........................................... 314
    II. The Variable Percentage Reduction Option.. 316
    A. EPA’s Authority Under Section 111 to Issue a Variable Standard ...........i............................ 318
    1. The Statutory Language.......................... 318
    2. The Legislative History............................. 319
    B. The Reasonableness of EPA’s Decision to Issue a Variable Standard............................. 322
    1. Technical Background............................... 323
    2. EPA’s Explanation for the Variable Standard....................................................... 325
    (a) The Factors Considered by EPA...... 325
    (b) EPA’s Regulatory Analysis.............. 326
    (c) EPA’s Stated Rationale for the Variable Standard ...................................... 327
    3. An Examination of EPA’s Rationale for the Variable Standard .............................. 328
    (a) The Legitimacy of EPA’s Regulatory Analysis....................................... 329
    (1) EPA’s Authority to Analyze Long Term National and Regional Impacts............................. 329
    (2) The Reliability of EPA’s Econometric Computer Model........... 332
    (b) The Reasonableness of EPA’s Conclusions ................................................ 336
    (1) The Reasonableness of EPA’s Conclusion that Variable Control Reflects a Better Balance of the Section 111 Factors Than Uniform Control ......................... 336
    
      Page
    (2) The Reasonableness of EPA’s Conclusion that Variable Control Promotes the Policies of the Act ........................................ 338
    C. The Dry Scrubbing Controversy.................... 340
    1. The Role of Dry Scrubbing Technology in EPA’s Rationale for the Variable Standard...................................’.................... 340
    2. The Legitimacy of Considering Emerging Technology in Setting Section 111 Standards .................................................... 346
    3. The Adequacy of the Record for Dry Scrubbing’s Role in EPA’s Rationale...... 347
    D. The Adequacy of Notice and the Opportunity to Comment on the Rationale for the Variable Standard.................................................... 352
    III. The 90 Percent Removal Standard................ 356
    A. Notice As to the Basis of the 90 Percent Standard............................................................. 356
    1. The Basis of the Final Standard............. 356
    2. Notice that the Basis of the Standard Had Changed Since Proposal................... 358
    B. The Achievability of the 90 Percent Standard ....................................................................... 360
    1. The Support For EPA’s Conclusions About FGD Performance ........................ 360
    (a) The Achievability of 92 Percent Long Term Removal Efficiency....... 361
    (b) The Reasonableness of EPA’s Assumption About FGD Variability...... 364
    2. The Support for EPA’s Conclusion that the 90 Percent Standard Was Achievable by the Use of Coal Washing in Conjunction with Scrubbing .................... 367
    (a) Description of the Coal Washing Process.................................................. 368
    (b) The Percentage Reduction Achievable by Washing High Sulfur Coal.. 369
    
      Page
    IV. The Standard for Emission of Particulate Matter .................................................................... 374
    A. Technical Background..................................... 374
    1. ESP Control Technology............................ 374
    2. Baghouse Control Technology................... 375
    B. The Evolution of the Particulate Standard.... 376
    C. The Achievability of the Standard................ 377
    1. EPA’s ESP Data........................................ 377
    2. EPA’s Baghouse Data .............................. 380
    V. The 1.2 Lbs./MBtu Emission Ceiling............ 384
    A. EPA’s Rationale for the Emission Ceiling.... 384
    B. EDF’s Procedural Attack............................... 386
    1. Late Comments .......................................... 387
    2. Meetings ....................................................... 387
    C. Standard for Judicial Review of EPA Procedures ............................................................... 391
    D. Statutory Provisions Concerning Procedure.. 392
    E. Validity of EPA’s Procedures During the the Post-Comment Period ............................. 396
    1. Written Comments Submitted During the Post-Comment Period......................... 397
    2. Meetings Held with Individuals Outside EPA ............................................................ 400
    (a) Intra-Executive Branch Meetings.... 404
    (b) Meetings Involving Alleged Congressional Pressure................................... 408
    VI. Conclusion ............................................................ 410
    Appendix............................................................................. 411
    Before ROBB, WALD and GINSBURG, Circuit Judges.
    Opinion for the Court filed by Circuit Judge WALD.
    Circuit Judge ROBB concurs in the result.
   WALD, Circuit Judge:

This case concerns the extent to which new coal-fired steam generators that produce electricity must control their emissions of sulfur dioxide and particulate matter into the air. In June of 1979 EPA revised the regulations called “new source performance standards” (“NSPS” or “standards”) governing emission control by coal burning power plants. On this appeal we consider challenges to the revised NSPS brought by environmental groups which contend that the standards are too lax and by electric utilities which contend that the standards are too rigorous. Together these petitioners present an array of statutory, substantive, and procedural grounds for overturning the challenged standards. For the reasons stated below, we hold that EPA did not exceed its statutory authority under the Clean Air Act in promulgating the NSPS, and we decline to set aside the standards.

I. INTRODUCTION

A. The Challenged Standards

The Clean Air Act provides for direct federal regulation of emissions from new stationary sources of air pollution by authorizing EPA to set performance standards for significant sources of air pollution which may be reasonably anticipated to endanger public health or welfare. In June 1979 EPA promulgated the NSPS involved in this case. The new standards increase pollution controls for new coal-fired electric power plants by tightening restrictions on emissions of sulfur dioxide and particulate matter. Sulfur dioxide emissions are limited to a maximum of 1.2 lbs./MBtu (or 520 ng/j) and a 90 percent reduction of potential uncontrolled sulfur dioxide emissions is required except when emissions to the atmosphere are less than 0.60 lbs./MBtu (or 260 ng/j). When sulfur dioxide emissions are less than 0.60 lbs./MBtu potential emissions must be reduced by no less than 70 percent. In addition, emissions of particulate matter are limited to 0.03 lbs./MBtu (or 13 ng/j).

B. The Parties

Petitioners in this case are Sierra Club and the State of California Air Resources Board (“CARB”), which oppose the variable 70 to 90 percent reduction requirement of the NSPS; Appalachian Power Co. (“APCO”), et a/., a group comprised of APCO, the Edison Electric Institute, the National Rural Electric Cooperative Association, and 86 individual utilities (“Electric Utilities”), which challenge both the maximum 90 percent reduction requirement and the 0.03 lbs./MBtu limit on emissions of particulate matter; and, the Environmental Defense Fund (“EDF”), which challenges the 1.2 lbs./MBtu ceiling imposed by the NSPS.

Intervenor-respondents filing briefs in these consolidated actions are the Electric Utilities and the Missouri Association of Municipal Utilities (“MAMU”), aligned in favor of both the variable percentage reduction standard and the 1.2 lbs./MBtu emissions ceiling; and the National Coal Association (“NCA”), which opposes EDP’s claim that the 1.2 lbs./MBtu ceiling is invalid due to procedural impropriety.

Respondents are the United States Environmental Protection Agency (“EPA”) and its Administrator, Douglas M. Costle.

C. Background

The importance of the challenged standards arises not only from the magnitude of the environmental and health interests involved, but also from the critical implications the new pollution controls have for the economy — at the local and national levels. Further heightening the significance of this controversy is the crucial role coal burning power plants are expected to play in our nation’s effort to cope with the problems associated with energy scarcity.

Coal is the dominant fuel used for generating electricity in the United States. When coal is burned, it releases sulfur dioxide and particulate matter into the atmosphere. At the very least these pollutants are known to cause or contribute to respiratory illnesses. In 1975 alone electric power plants emitted 18.6 million tons of sulfur dioxide. If the former NSPS had not been changed the total annual national sulfur dioxide emissions could have exceeded 23 million tons by 1995: a 27 percent increase. The increase in emissions which could be expected if the former standards continued in effect would be more dramatic on a regional basis. For example, utility sulfur dioxide emissions could be expected to increase 1300 percent by 1995 in the West South Central region of the country (Texas, Oklahoma, Arkansas, and Louisiana). In 1976 power plant emissions accounted for 64 percent of the total estimated sulfur dioxide emissions and 24 percent of the total estimated particulate matter emissions in the entire country.

EPA’s revised NSPS are designed to curtail these emissions. EPA predicts that the new standards would reduce national sulfur dioxide emissions from new plants by 50 percent and national particulate matter emissions by 70 percent by 1995. The cost of the new controls, however, is substantial. EPA estimates that utilities will have to spend tens of billions of dollars by 1995 on pollution control under the new NSPS. Consumers will ultimately bear these costs, both directly in the form of residential utility bills, and indirectly in the form of higher consumer prices due to increased energy costs. Coinciding with these trends the utility industry is expected to have continued and significant growth. Under the new NSPS EPA projects that overall utility capacity should increase by about 50 percent with approximately 300 new fossil-fuel fired power plants to begin operation within the next ten years. And approximately 350 new plants (capable of generating 250 Gigawatts (“GW”)) are expected to be constructed by 1995. Present levels of national coal production and consumption will triple by 1995. With oil scarce, the future of nuclear and solar energy uncertain, and hydro limited, “the nation’s rich and cheap coal reserves call for exploitation.” Not surprisingly, coal burning power plants’ already preeminent share of electric power produced in the United States will grow over the remainder of this century.

While the volume and technical complexity of the material necessary for our review is daunting we have endeavored to consider thoroughly the claims and myriad arguments proffered by the parties. We will discuss the basis of our decision on the principal challenges of the parties. We will not attempt, however, to discuss each and every point briefed, nor do we feel compelled to adhere religiously to the analytic framework devised by the parties.

D. Procedural History

In 1970 Congress for the first time authorized the federal government to set performance standards limiting emissions from newly built or modified sources of air pollution. These sources to be controlled were those that EPA determined emitted pollution contributing substantially to the endangerment of the public health or welfare. EPA decided that large coal-fired generators fell within that category. In December 1971 EPA issued a NSPS for these sources. That first NSPS applied to units capable of firing more than 250 MBtu per hour, and limited sulfur dioxide emissions to 1.2 lbs./MBtu and particulate matter emissions to 0.10 lbs./MBtu. Under this standard it was possible to satisfy the emission limitations simply by burning coal with a low sulfur content.

In 1976 the Sierra Club and the Oijato and Red Mesa Chapters of the Navajo Tribe petitioned EPA to revise the NSPS so as to require a 90 percent reduction in sulfur dioxide emissions. The petition claimed that advances in technology since 1971 justified a revision of the standard. In response to the petition EPA began an investigation of whether the standard should be changed.

While EPA’s decision was pending the Clean Air Act Amendments of 1977 were signed into law. Section 111 of the amendments, discussed more fully below, required EPA to revise the standards of performance for electric power plants within one year after the August 1977 enactment date. When it appeared that EPA would not meet this deadline, the Sierra Club filed a complaint in the District Court for the District of Columbia. The court approved a stipulation requiring the proposed regulations to issue in September 1978, and promulgation of final regulations within six months after the proposal. Eventually, after further delay, the final NSPS were promulgated in June 1979.

Several parties petitioned EPA for reconsideration of the revised NSPS. In February of 1980 EPA denied all the petitions for reconsideration.

The present appeal followed. Petitions for review of the NSPS were filed in this court by the Electric Utilities (No. 79-1719), Sierra Club (No. 79-1565), EDF (No. 79-1874), and CARB (No. 79-1867). In addition, petitions to review EPA’s denial of the requests for reconsideration of the final NSPS were filed by the Electric Utilities (No. 80-1187), Sierra Club (No. 80-1201), EDF (No. 80-1213), and CARB (No. 80-1338). All of these cases have been consolidated.

II. THE VARIABLE PERCENTAGE REDUCTION OPTION We have already noted that the final NSPS adopted by EPA include an optional variable percentage reduction standard. Under this optional standard a utility plant can permissibly reduce its sulfur dioxide emissions by less than 90 percent of potential uncontrolled emissions if the amount of sulfur dioxide emitted following the use of pollution control technology is less than 0.60 lbs./MBtu. In no instance, however, can a plant reduce emissions by less than 70 percent of potential uncontrolled emissions. As a result of this option, the NSPS requirements for percentage reduction of sulfur dioxide removal vary on a sliding scale ranging from a minimum of 70 percent to a maximum of 90 percent. There is no dispute that the 70 percent floor in the standard necessarily means that, given the present state of pollution control technology, utilities will have to employ some form of flue gas desulfurization (“FGD” or “scrubbing”) technology.

Sierra Club contests EPA’s authority under section 111 of the Act to vary from a uniform national percentage reduction standard (“uniform standard” or “full control”) and the reasonableness of EPA’s justification for doing so in light of the administrative record. Additionally, Sierra Club argues that the variable standard is fatally flawed and must be set aside regardless of supporting evidence on the record because the rulemaking was procedurally defective. The procedural objections to the variable control component of the NSPS stem from Sierra Club’s assertion that EPA did not give adequate notice of the basis for the variable standard or provide sufficient opportunity for adversarial comment on the agency’s purported justification for the rule. We turn to the question of EPA’s statutory authority first.

A. EPA’s Authority Under Section 111 to Issue A Variable Standard

Sierra Club’s challenge to variable control raises the fundamental issue of whether EPA violated section 111 of the Clean Air Act by establishing a sliding scale for the reduction of sulfur dioxide emissions based on the sulfur content of coal burned in new utility plants. We find that section 111 of the Act authorizes such a variable standard.

1. The Statutory Language

To evaluate the competing interpretations of section 111 we turn first to its text Initially we find that the language of section 111 neither imposes a single, nationally uniform, percentage reduction standard nor prohibits EPA from varying the standard. Rather, section 111 merely requires inter alia:

[T]he achievement of a percentage reduction in the emissions from such category of sources [like new coal burning utility plants] from the emissions which would have resulted from the use of fuels which are not subject to treatment prior to combustion ....

The absence of any express mandate in this language to adhere to a single percentage reduction standard critically undercuts Sierra Club’s arguments that EPA could not vary the standard below the level which is technologically feasible.

In fact, EPA is expressly authorized by section 111 to “distinguish among classes, types and sizes within categories of new sources for the purpose of establishing . . . standards.” Thus, the statute provides on its face that EPA does not have to set a uniform percentage reduction requirement for an entire category of emission sources. On the basis of this language alone, it would seem presumptively reasonable for EPA to set different percentage reduction standards for utility plants that burn coal of varying sulfur content. Certainly the text of the statute nowhere forbids a distinction based on sulfur content.

Other provisions of section 111 also belie the notion that EPA lacks discretion to vary the percentage reduction requirement according to the sulfur content of coal. For example, section 111(a) explicitly instructs EPA to balance multiple concerns when promulgating a NSPS:

[A] standard of performance shall reflect the degree of emission limitation and the percentage reduction achievable through application of the best technological system of continuous emission reduction which (taking into consideration the cost of achieving such emission reduction, any nonair quality health and environmental impact and energy requirements) the Administrator determines has been adequately demonstrated.

(Emphasis supplied.) Having given EPA this mandate, Congress surely could not have meant to bind the agency to issuance of a uniform standard even though the agency’s balancing of cost, energy, and non-air quality health and environmental factors indicated that the percentage standard should vary according to the sulfur content of coal.

Furthermore, reading section 111 to permit a variable standard based on the sulfur content of coal comports with common sense which suggests that the amount of sulfur in coal is the most relevant factor in designing standards to reduce emissions of sulfur in the gaseous wastes of coal combustion. Quite obviously, the “best technological system,” considering cost, energy, and nonair health and environmental factors may well vary depending on the sulfur content of the coal that is burned.

2. The Legislative History

Sierra Club relies on portions of the legislative history of the 1977 Amendments to the Clean Air Act to demonstrate that, no matter how logical it may seem to permit the percentage reduction standard to vary according to the sulfur content of coal burned by utilities, Congress nevertheless meant to forbid such variable control levels. But the statements in the legislative history Sierra Club cites to us, even assuming that they are entitled to substantial weight in the face of a relatively clear text, do not adequately support Sierra Club’s interpretation of the Act.

We note initially that a specific percentage reduction requirement was added to the text of section 111 only by the Conference Committee after the bills had passed both Houses of Congress. The Conference Committee Report explaining the requirement clearly contemplated the adoption of a variable standard:

[T]he Conferees agreed that the Administrator may, in his discretion, set a range of pollutant reduction that reflects varying fuel characteristics. Any departure from the uniform national percentage reduction requirement, however, must be accompanied by a finding that such a departure does not undermine the basic purposes of the House provision and the other provisions of the act, such as maximizing the use of locally available fuel.

(Emphasis supplied.) Subsequently, during the House consideration of the Report the Conference Committee submitted a “Clarifying Statement” which stated that it was only fuel characteristics that could justify a departure from uniform control:

While the Conferees agreed that the Administrator may set the percentage reduction requirement as a percentage range, the Conferees expect the Administrator to be exceedingly cautious if he should elect to do so. Any such range of percent reduction would be allowed only to reflect varying fuel characteristics, and must be based on a carefully and completely documented finding by the Administrator that such departure from the strict requirement does not undermine the basic purposes of the House provision as expressed on pages 183 through 195 of the House Report number 95-294.

(Emphasis supplied.) Similarly, Senate consideration of the Report included a Clarifying Statement by Senator Muskie that recognized a variable range of percentage reduction was permissible:

EPA’s Administrator is given the flexibility to set a range of pollutant removal based on varying fuel characteristics if he finds that the NSPS objectives [of the Act] are not undermined.

(Emphasis supplied.)

Even in the face of this legislative history, however, Sierra Club contends that “it is crystal clear that sulfur content of coal was not to be one of the ‘varying fuel characteristics’ which would justify a departure from a uniform standard.” We are frankly at a loss to understand this statement. Neither the remarks of Representative Rogers, the House manager, nor Senator Muskie, the Senate manager, when introducing the Conference Committee Reports to their respective Houses, supports Sierra Club’s narrow interpretation of the phrase “fuel characteristic” to exclude sulfur content. Sierra Club relies on Senator Domenici’s “additional statement” submitted after the close of the floor debate on the Senate version of the bill (S. 252) — before the bill went to Conference — which reads in part:

The House amendments to the Clean Air Act (H.R. 6161) contain a provision — section 111 — that effectively requires all new coal-fired powerplants to meet the same percentage reduction of pollution removal on new powerplants regardless of the sulfur content of the coal burned. Any doubts on this matter are dispelled by the explicit report language.

(Emphasis supplied.) When read in context, however, it is clear that Senator Domenici was arguing that the Senate should not acquiesce in Conference to any demand for a uniform percentage reduction applied to all coals which he believed was implied in the House bill. Sierra Club’s reliance on this statement is misplaced because the statement was made before the Conference Committee met at a time when neither the House nor the Senate bill contained any express provision for a percentage reduction. In fact, Senator Domenici’s views opposing a uniform standard based on sulfur content can be viewed as a motivating factor in the Conference Committee’s adoption of a more flexible standard in the final bill that allowed such a variation. Nothing else in the legislative history comes close to a directive that sulfur content is not a relevant fuel characteristic for setting a variable standard.

Sierra Club also argues that even if section 111 permits the standard to vary depending on the sulfur content of coal, its language was designed to permit a nonuniform standard only in the limited circumstance where a “best technological system” could not achieve the national percentage on certain types of coal. That is, EPA could vary the standard only to reflect the different maximum feasible percentage reductions achievable for different sulfur content coals. Under this view EPA could not relax the standard when a higher percentage reduction is technologically feasible. Thus, in this case because it is not disputed that wet scrubbing could achieve 90 percent reduction on low sulfur coal, EPA has no authority to vary the standard below the 90 percent level.

We do not believe that this interpretation of section 111 is warranted by a fair reading of the Act or the underlying legislative history. The text gives EPA broad discretion to weigh different factors in setting the standard. The legislative history indicates that EPA should be “exceedingly cautious” in allowing the standard to vary, but nevertheless, recognizes that such a determination is within the range of EPA’s discretion. The required finding that must underlie a variable standard is much broader than a mere determination that uniformity is not achievable. Rather, EPA has the discretion to vary the standard upon finding “that such a departure [from uniform control] does not undermine the basic purposes of the Act.” Here EPA has made such a finding. While the reasonableness of this finding is challenged on this appeal and will be reviewed below, here it cannot be said that in making the determination EPA acted beyond its statutory authority.

In addition to its arguments about the proper interpretation of section 111, Sierra Club maintains that variable control violates the total statutory scheme of the Clean Air Act because it is irreconcilable with other important features of the 1977 Amendments to the Act. In particular, Sierra Club contends that variable control is inherently inconsistent with the provisions in the Act designed to prevent the deterioration of air quality and visibility in designated areas, primarily in the Southwest. EPA responds first that, in fact, the variable standard is consistent with the other programs established by the Clean Air Act. This argument is grounded in the extensive regulatory analysis performed by EPA which showed that variable control served the interests of air quality and visibility as well as any uniform standard. We save for later our review of the legitimacy of that regulatory analysis and the reasonableness of EPA’s conclusion that the variable standard actually promotes improved air quality and visibility. At this point, we note that if its analysis is reasonable, then EPA is right and the variable standard does not conflict with other goals. Second, EPA argues convincingly that the variable standard does not infringe the other special programs' of the Act, even if variable control would result in some decreases in air quality and visibility in certain parts of the country. This is because the NSPS authorized in section 111(a) are but one of many Clean Air Act requirements that might be applied by EPA or state agencies to new plants. To the extent that theré are localized problems with air quality and visibility under national NSPS, the Act permits more stringent requirements to be applied in problem areas in addition to the NSPS. Thus, accepting arguendo Sierra Club’s view of the facts — that the new NSPS would not foster air quality and visibility in certain specially protected areas — it still cannot be held as a matter of law that the standard must fail because it impedes the other statutory mechanisms for coping with these local problems.

We find, in sum, that EPA has the authority under section 111 of the Act to promulgate the variable standard and now turn to a consideration of whether EPA’s decision to adopt the variable standard was reasonable and supported by the record.

B. The Reasonableness of EPA’s Decision to Issue a Variable Standard

In reviewing the merits of EPA’s variable standard, our function is to ensure that “the agency, given an essentially legislative task to perform, has carried it out in a manner calculated to negate the dangers of arbitrariness and irrationality in the formulation of rules ... for the future.” If we find EPA's choice of variable control to be arbitrary and capricious then we will set the standard aside. We do not consider the policy issues de novo, substituting our judgment for that of the agency, but evaluate whether the agency has exercised reasoned discretion. This means that the agency must consider all of the relevant factors and demonstrate a reasonable conneetion between the facts on the record and the resulting policy choice.

1. Technical Background

The controversy over EPA’s justification for variable control centers on two processes for flue gas desulfurization (“FGD” or “scrubbing”) referred to by the parties as wet scrubbing and dry scrubbing. Scrubbing, in contrast to other techniques for reduction of sulfur emission from coal combustion, involves the maintenance of a large scale chemical reaction to clean the smoke produced by coal combustion. Typically, as exhaust gases flow up a power plant smokestack, they are exposed to an absorbent medium that is sprayed in their path. Sulfur dioxide in the gas reacts with the chemical absorbent and takes a form which can be collected and removed from the exhaust.

The type of wet scrubbing process relied on by EPA during this rulemaking was a “properly designed, installed, operated and maintained” lime or limestone FGD system. This wet scrubbing system requires that large quantities of lime or ground limestone be mixed with water to form a slurry. The slurry is sprayed into flue gas and absorbs sulfur dioxide which reacts with the slurry to form precipitates (predominantly calcium sulfite and calcium sulfate), which are in turn removed, dewatered, and disposed of in the form of sludge. A simplified flow diagram of a wet lime/limestone system is shown as Figure 1 in the appendix to this opinion.

Dry scrubbing is a newer and relatively less established technological alternative to wet lime/limestone scrubbing systems. Interest in developing dry scrubbing has been stimulated by perceived advantages over wet scrubbing. The dry scrubbing design which EPA focused on during the rulemaking removes sulfur dioxide in two stages which incorporate the use of a spray dryer and a baghouse. In this system a spray dryer (similar to a wet scrubber) is used with lime, soda ash, or other reagents to scrub sulfur dioxide from flue gases. Unlike wet scrubbing systems, since the flue gas leaving the spray dryer is “hot” (150-180° F) due to the minimal use of water in the spray dryer (by design), no additional reheating of the exhaust plume is required. Following the spray dryer, a baghouse is used to collect all particulate matter (including sulfur dioxide reactants). Simplified flow diagrams of typical dry scrubbers are shown as Figures 2 and 3 in the appendix to this opinion.

2. EPA’s Explanation for the Variable Standard

(a) The Factors Considered By EPA

While the parties dispute the proper analytic method for balancing the relevant factors, they agree, with one exception, on the factors themselves which are relevant to EPA’s decision to issue the variable standard. These factors are enumerated in section 111 of the Act and in the legislative history.

Section 111(a)(1), as revised in 1977, requires EPA to weigh cost, energy, and non-air quality health and enviromental factors in setting a percentage reduction standard achievable by the best technological system of continuous emission reduction. During its passage through Congress the Conferees issued a clarifying statement that EPA may promulgate a variable percentage reduction standard so long as the agency determines that the standard does not undermine the essential purposes of the Act. The parties agree that these purposes are as follows:

1. The standards must not give a competitive advantage to one State over another in attracting industry.
2. The standards must maximize the potential for long-term economic growth by reducing emissions as much as practicable. This would increase the amount of industrial growth possible within the limits set by the air quality standards.
3. The standards must to the extent practical force the installation of all the control technology that will ever be necessary on new plants at the time of construction when it is cheaper to install, thereby minimizing the need for retrofit in the future when air quality standards begin to set limits to growth.
4 and 5. The standards to the extent practical must force new sources to burn high-sulfur fuel thus freeing low-sulfur fuel for use in existing sources where it is harder to control emissions and where low-sulfur fuel is needed for compliance. This will (1) allow old sources to operate longer and (2) expand environmentally acceptable energy supplies.
6. The standards should be stringent in order to force the development of improved technology.

Sierra Club objects that EPA also took account of the impact of alternative standards on future national levels of sulfur dioxide emissions. Paradoxically, Sierra Club argues that “EPA may not consider total air emissions in deciding on a proper NSPS.” Sierra Club reasons that by specifying only nonair quality health environmental considerations in section 111 Congress meant to exclude EPA's discretion to consider air quality effects of different standards.

We find this position untenable given that one of the agreed upon legislative purposes, set out above, requires that the standards must maximize the potential for long term economic growth “by reducing emissions as much as practicable.” (Emphasis supplied.) In any event, we can think of no sensible interpretation of the statutory words “best technological system” which would not incorporate the amount of air pollution as a relevant factor to be weighed when determining the optimal standard for controlling sulfur dioxide emissions. Control technologies cannot be “best” if they create greater problems than they solve. In fact, we do not see how we could uphold a variable standard if EPA had not evaluated its effect on air emissions.

(b) EPA’s Regulatory Analysis

EPA performed a regulatory analysis in three phases to evaluate alternative standards. Phase one of the analysis began before EPA published its proposed standards. Prior to framing alternative standards for consideration, EPA evaluated different control technologies in terms of performance, costs, energy requirements and environmental impacts. EPA also performed a preliminary study of these factors at the national, regional and plantsite levels and toward this end employed econometric computer models to forecast the nature of the utility industry in future years. The initial modeling effort was completed in April 1978 and revised in August 1978.

After this preliminary analysis EPA proposed a uniform 85 percent reduction standard while reserving judgment on whether the uniform percentage reduction standard was preferable to several alternative standards. EPA announced that the final decision would await additional analysis and public comment on the proposal. At that time the agency also announced that five methods of “wet” scrubbing were adequately demonstrated and that these technologies could all attain the proposed 85 percent limitation. The ensuing rulemaking thus focused not on which technology should be employed, but on the appropriate level of control.

The regulatory analysis entered phase two following the September 1978 proposal. EPA conducted additional analyses of the impacts of alternative sulfur dioxide standards. The impacts analyzed included total air emissions, utility investment in new plant and pollution equipment, consumer costs, energy production and consumption, coal use, utility consumption of oil and natural gas, and the amount of western low sulfur coal shipped East. In addition, supplementary analyses were performed to assess the impact of alternative emission ceilings on specific regional coal reserves, to verify the performance characteristics of alternative scrubbing technologies, and to assess the sulfur reduction potential of coal preparation techniques. As part of the phase two analysis, a joint working group comprised of representatives from EPA, the Department of Energy, the Council of Economic Advisors, the Council on Wage and Price Stability, and others reviewed the underlying assumptions of the econometric model used in the August 1978 analysis and worked to develop new standards for testing in the computer model. As a result of the joint working group’s efforts some assumptions were changed and a number of alternative standards were defined and considered. During phase two EPA also considered public comments on the proposal, identified critical parameters of uncertainty in the model, and revised the model so as to incorporate new considerations such as credits for coal washing which previously had not been properly accounted for in the model. The results of the phase two analysis were published and discussed at a public hearing in December 1978.

Phase three of EPA’s regulatory analysis occurred after the public hearing and after the close of the formal comment period on the proposed NSPS. This third stage featured for the first time EPA’s formal consideration through its computer model of the impacts of dry scrubbing technology, a subject which will be discussed at length below. During phase three the model was run to forecast the impacts of each potential standard, first assuming the use of wet scrubbers only, and then assuming that utilities would use dry scrubbers in situations where it was economically and technologically feasible to do so. EPA obtained separate results under the alternative wet scrubbing and dry scrubbing assumptions. In brief, the phase three modeling analysis indicated that “[t]he variable control option produces emissions that are equal to or lower than the other options under both the wet scrubbing and dry scrubbing assumptions.” Further, under the wet and dry assumptions, variable control as compared to uniform control was predicted to result in more coal capacity in newer and “cleaner” utility plants, to have a clear cost advantage, to use less oil, and to have an equivalent impact on coal production.

(c) EPA’s Stated Rationale for the Variable Standard

EPA’s explanation for the adoption of the variable standard is contained in a long preamble accompanying the publication of the final NSPS. EPA stated that comments received from advocates of variable control supported a departure from uniform control principally on the basis that variable control “best satisfies the statutory language of Section 111 because it would achieve virtually the same emission reductions at a national level as a uniform approach but at substantially lower costs.” “In addition [the commentators] argue that a variable control option would provide a better opportunity for the development of . . . dry SO2 control systems which they felt held considerable promise for bringing about S02 emission reductions at lower costs and in a more reliable manner.” These comments, EPA explained, were the impetus for the phase three modeling analysis. EPA concluded that the results of this further analysis, as reported in the preamble and scrutinized below, demonstrated that the variable control option was best. EPA justified the variable standard in terms of the policies of the Act as follows:

The standard reflects a balance in environmental, economic, and energy consideration by being sufficiently stringent to bring about substantial reductions in SO2 emissions (3 million tons in 1995) yet does so at reasonable costs without significant energy penalties. When compared to a uniform 90 percent reduction, the standard achieves the same emission reductions at the national level. More importantly, by providing an opportunity for full development of dry S02 technology the standard offers potential for further emission reductions (100 to 200 thousand tons per year), cost savings (over $1 billion per year), and a reduction in oil consumption (200 thousand barrels per day) when compared to a uniform standard. The standard through its balance and recognition of varying coal characteristics, serves to expand environmentally acceptable energy supplies without conveying a competitive advantage to any one coal producing region. The maintenance of the emission limitation at 520 ng/j (1.2 lb SO2 million Btu) will serve to encourage the use of locally available high-sulfur coals. By providing for a range of percent reductions, the standard offers flexibility in regard to burning of intermediate sulfur content coals. By placing a minimum requirement of 70 percent on low-sulfur coals, the final rule encourages the full development and application of dry S02 control systems on a range of coals. At the same time, the minimum requirement is sufficiently stringent to reduce the amount of low-sulfur coal that moves eastward when compared to the current standard. Admittedly, a uniform 90 percent requirement would reduce such movements further, but in the Administrator’s opinion, such gains would be of marginal value when compared to expected increases in high-sulfur coal production. By achieving a balanced coal demand within the utility sector and by promoting the development of less expensive S02 control technology, the final standard will expand environmentally acceptable energy supplies to existing power plants and industrial sources.
By substantially reducing S02 emissions, the standard will enhance the potential for long term economic growth at both the national and regional levels. While more restrictive requirements may have resulted in marginal air quality improvements locally, their higher costs may well have served to retard rather than promote air quality improvement nationally by delaying the retirement of older, poorly controlled plants.
The standard must also be viewed within the broad context of the Clean Air Act Amendments of 1977. It serves as a minimum requirement for both prevention of significant deterioration and non-attainment considerations. When warranted by local conditions, ample authority exists to impose more restrictive requirements through the case-by-case new source review process. When exercised in conjunction with the standard, these authorities will assure that our pristine areas and national parks are adequately protected. Similarly, in those areas where the attainment and maintenance of the ambient air quality standard is threatened, more restrictive requirements will be imposed.

Sierra Club insists that EPA’s conclusions about dry scrubbing technology are in effect the “cornerstone” of the variable standard. Therefore, Sierra Club argues, the standard must be judged solely on the basis of the validity of EPA’s so-called dry scrubbing rationale. We do not agree and believe that it is appropriate to focus on the statutory, substantive, and procedural issues surrounding the dry scrubbing controversy in a later section of this opinion. For now we address Sierra Club’s challenges to the standard which are independent of the questions raised about the role of dry scrubbing in the outcome of the final rule.

3. An Examination of EPA’s Rationale for the Variable Standard

Sierra Club challenges both EPA’s findings about the relative national and regional impacts of alternative standards and the conclusions the agency drew from these findings. First, Sierra Club raises a number of overlapping arguments in support of its view that the findings themselves are methodologically defective. Sierra Club’s position, as we understand it, is that the findings cannot amount to substantial evidence because the agency’s regulatory analysis which generated the findings was ill-conceived and impermissible under the Act. Specifically, Sierra Club objects to the conceptual framework by which EPA took account of the cost, energy, and environmental considerations mandated by section 111 of the Act. In addition, Sierra Club asserts that the econometric model employed by EPA was so speculative and otherwise unreliable that the modeling results are not substantial evidence. Finally, even accepting EPA’s findings, Sierra Club contests EPA’s judgment that the variable standard promotes the objectives of the Act. We address these questions seriatim.

(a) The Legitimacy of EPA’s Regulatory Analysis

(1) EPA’s Authority to Analyze Long Term National and Regional Impacts

Sierra Club argues that section 111 only allows EPA to weigh the cost, energy, and nonair quality health and environmental impacts specified in the statute in order to identify the “best technology.” Once that technology is selected, according to Sierra Club, the standard must be set at whatever level is “achievable” by such technology, i. e., the maximum technologically feasible level of control. In this case, since EPA designated wet scrubbing as the technology of choice, the standard must be set at the maximum control level achievable by wet scrubbing. Sierra Club maintains that the kind of macrobalancing EPA has performed has already been done by Congress, and that Congress decided, as reflected in the language of section 111, to require the fullest degree of control that is achievable by the “best technological system” — in this case, a uniform reduction standard of at least 90 percent. The only comparison of aggregate impacts by EPA which Sierra Club believes would have been legitimate under section 111 is a comparison between the impacts of full scrubbing low sulfur coal and the impacts of full scrubbing high sulfur coal. Since there is no doubt that wet scrubbing low sulfur coal is more economical, uses less energy and has fewer other detrimental consequences than wet scrubbing high sulfur coal, Sierra Club argues that this comparison, if anything, demonstrates that the percentage reduction standard should be higher for low sulfur coal than for high sulfur coal. Sierra Club also objects that EPA improperly projected long range future impacts of alternative standards and “insists that the only factors which may be considered by EPA are the technological, economic, environmental, and energy impacts of presently existing technology.”

We reject Sierra Club’s restrictive reading of the balancing exercise mandated by section 111 as too narrow to accomplish the purposes of the Act. This is so for several reasons.

1. Sierra Club’s interpretation of section 111 is internally inconsistent. Sierra Club would permit EPA to consider the enumerated statutory factors only for the purpose of defining the best technology. This exercise, however, would necessarily involve evaluating the cost, energy, and environmental impacts of different technological systems — not in the abstract — but at some given level of operation. Thus, even the limited determination that Sierra Club would allow EPA to make would logically involve determining at what level a particular control system was “best” in terms of cost, environment, and energy. And so Sierra Club’s argument that section 111 requires the standard to be set at 90 percent or higher in the case of wet scrubbing (if technologically achievable) would not follow if wet scrubbing at 85 percent removal efficiency was the “best” in terms of the statutory factors. In short, there is simply no way to set the standard at the level of maximum technological feasibility while simultaneously responding to the cost, energy, and environmental concerns that Congress wrote upon the face of the statute.

2. The language of section 111 not only authorizes variable control but also gives EPA authority when determining the best technological system to weigh cost, energy, and environmental impacts in the broadest sense — at the national and regional levels and over time as opposed to simply at the plant level in the immediate present. The pertinent portion of section 111 reads:

[A] standard of performance shall reflect the degree of emission limitation and the percentage reduction achievable through application of the best technological system of continuous emission reduction which (taking into consideration the cost of achieving such emission reduction, any nonair quality health and environmental impact and energy requirements) the Administrator determines has been adequately demonstrated.

The extraordinary clumsiness of the phrasing of this section does not ease our task of interpretation. Nevertheless, we believe it is clear that this language is far different from the words Congress would have chosen to mandate that EPA set standards at the maximum degree of pollution control technologically achievable. Parsed, section 111 most reasonably seems to require that EPA identify the emission levels that are “achievable” with “adequately demonstrated technology.” After EPA makes this determination, it must exercise its discretion to choose an achievable emission level which represents the best balance of economic, environmental, and energy considerations. It follows that to exercise this discretion EPA must examine the effects of technology on the grand scale in order to decide which level of control is best. For example, an efficient water intensive technology capable of 95 percent removal efficiency might be “best” in the East where water is plentiful, but environmentally disastrous in the water-scarce West where a different technology, capable of only 80 percent reduction efficiency might be “best.” We cannot believe that Congress meant for EPA to ignore such future aggregate impacts of alternative standards. The standard is, after all, a national standard with long-term effects.

It seems likely that if Congress meant to require a monolithic standard and to curtail EPA’s discretion to weigh various policy considerations it would have explicitly said so in section 111, as it did in other parts of the statute. For instance, in prescribing standards for areas that have not succeeded in meeting national ambient air quality standards (“nonattainment areas”) Congress required that the standard be the “lowest achievable emission rate,” and stressed that cost factors, while still cognizable, were not to play as important a role as they do in selecting the “best” system under section 111.

3. In addition, when section 111 was amended in 1977 Congress did not narrow EPA’s discretion to perform broad based analysis of potential impacts of a standard, even though Congress was aware that previous administrative and judicial interpretations of the former version of section 111 permitted the assessment of the long term costs to industry, consumers, and the environment. In Essex Chemical Corp. v. EPA, and in Portland Cement Co. v. EPA this court specifically endorsed a broad interpretation of “costs” when it held that section 111 did not require a National Environmental Policy Act impact statement. Essential to the court’s reasoning was the understanding that “section 111 of the Clean Air Act, properly construed, requires the functional equivalent of a NEPA impact statement.” The court explained:

The standard of the “best system” is comprehensive, and we cannot imagine that Congress intended that “best” could apply to a system which did more damage to water than it prevented to air.

Largely as a result of Portland Cement, the “cost” considerations of former section 111 were specifically supplemented by Congress in the 1977 Amendments to cover considerations of nonair quality health and environmental impacts and energy requirements. In so doing, Congress made no attempt to cut back on EPA’s ability to apply the new terms broadly nor did Congress reduce the range of discretion that had been read previously into the “cost” factor.

4. The legislative history clearly supports our reading of amended section 111 as authorizing EPA to balance long term national and regional impacts of alternative standards. The Conferees defined the best technology in terms of “long-term growth,” “long-term cost savings,” effects on the “coal market,” including prices and utilization of coal reserves, and “incentives for improved technology.” Indeed, the Reports from both Houses on the Senate and House bills illustrate very clearly that Congress itself was using a long-term lens with a broad focus on future costs, environmental and energy effects of different technological systems when it discussed section 111.

5. Broad analysis of alternative standards promotes the several purposes of the Act articulated in the legislative history which Sierra Club recognizes are relevant to the decision to adopt the variable standard. In stating those purposes, Congress indicated that it wanted assurances from EPA that the new standards would not exacerbate existing problems, e. g., produce adverse effects on the coal market, impediments to long term growth, and inhibition of technological innovation. Congress could not have expected such complex interconnecting goals to be satisfied or even approximated without affording EPA a great deal of elbow room to react to and plan for changing events. If EPA was to do as Sierra Club suggests, and set the standard according to the single factor of technological achievability then EPA could not even begin to intelligently balance the stated purposes of the Act.

6. Finally, it is sensible for EPA to assess the likely impacts of the NSPS in 1995 as opposed to an earlier time. Since the standard is only applicable to “new sources” the standard will not have a measurable effect until there are a significant number of new plants in operation. EPA found that this will not occur until 1995 and explained:

Beyond 1995, our data show that many of the power plants on line today will be approaching retirement age. As utilization of older capacity declines, demand will be picked up by newer, better controlled plants. As this replacement occurs, national S02 emissions will begin to decline. Based on this projection, the Administrator believes that the 1990-1995 time frame will represent the peak years for S02 emissions and is, therefore, the relevant time frame for this analysis.

For all of these reasons we conclude that EPA was justified in relying on long term analysis of national and regional cost, environmental, and energy impacts of alternative percentage reduction standards in order to select the “best technological system” upon which to base the NSPS.

(2) The Reliability of EPA’s Econometric Computer Model

We are more sympathetic to Sierra Club’s complaint about the reliability of EPA’s econometric model. Such models, despite their complex design and aura of scientific validity, are at best imperfect and subject to manipulation as EPA forthrightly recognizes. The results ultimately are shaped by the assumptions adopted at the outset, and can change drastically for a given range of input data if key assumptions are adjusted even slightly. The accuracy of the model’s predictions also hinges on whether the underlying assumptions reflect reality, which is no small feat in this volatile world.

Still we cannot agree with Sierra Club that it was improper for EPA to employ an econometric computer model, or hold as a matter of law that EPA erred by relying on the model to forecast the future impacts of alternative standards fifteen years hence.

Realistically, computer modeling is a useful and often essential tool for performing the Herculean labors Congress imposed on EPA in the Clean Air Act. In addition to the competing objectives that EPA must satisfy under section 111, the Act explicitly requires EPA to prepare an Economic Impact Statement before promulgating NSPS. The assessment of potential impacts in this statement must be as “extensive as practicable” and must determine the potential inflationary or recessionary effects of the standard, the effects on competition, consumer costs, and energy use. Given the complexity and magnitude of the analyses EPA must perform on economic impacts alone, computer modeling, for all its flaws, is invaluable.

Even absent such statutory requirements, we would deem it reasonable to use computer modeling, and to design the model to consider not just “present day” factors, but the consequences over time of the proposed agency action. In American Public Gas Ass’n v. FPC, a challenge was raised that the results of economic modeling, similar to that used here, did not rise to the level of “substantial evidence” necessary to support the agency’s findings and conclusions. This court disagreed, stating that “[Reasoned decisionmaking can use an economic model to provide useful information about economic realities. ...” However, the agency must sufficiently explain the assumptions and methodology used in preparing the model; it must provide a “complete analytic defense of its model [and] respond to each objection with a reasoned presentation.” The technical complexity of the analysis does not relieve the agency of the burden to consider all relevant factors and to identify the stepping stones to its final decision. There must be a rational connection between the factual inputs, modeling assumptions, modeling results and conclusions drawn from these results.

In this case, the utility model itself and its key assumptions were discussed in the proposed rule and background documents. EPA invited public comments on the model and its assumptions, with the agency recognizing the sensitivity of the model to a “few key initial assumptions.” The joint interagency working group reviewed results of model runs, revised assumptions, and required new runs of the model when it was deemed appropriate. The principal comments received by EPA on the model and the initial assumptions were discussed, together with the results of the three phases of the modeling and the major post-proposal changes to the model, in the preamble to the final NSPS. In reviewing this record on the use of the econometric model we have carefully examined, within the limits of our competence, EPA’s explanation for the model’s premises, the results, and the conclusions drawn therefrom to test them for internal consistency and reasonableness. Although EPA has the benefit of the presumption of good faith and regularity in agency action, we have attempted to ascertain whether the results have been improperly skewed by the modeling format. We conclude that EPA’s reliance on its model did not exceed the bounds of its usefulness and that its conduct of the modeling exercise was proper in all respects. We are in fact reassured by EPA’s own consciousness of the limits of its model, and its invitation and response to public comment on all aspects of the model. The safety valves in the use of such sophisticated methodology are the requirement of public exposure of the assumptions and data incorporated into the analysis and the acceptance and consideration of public comment, the admission of uncertainties where they exist, and the insistence that ultimate responsibility for the policy decision remains with the agency rather than the computer. With these precautions the tools of econometric computer analysis can intelligently broaden rather than constrain the policymaker’s options and avoid the “artificial narrowing of options that [can be] arbitrary and capricious.”

Sierra Club has not only challenged the use of the model itself, but has also questioned here, as it has throughout the rulemaking, some of the specific assumptions built into the model. In some instances EPA actually adjusted the model to account for Sierra Club’s objections and demonstrated that the outcome of the final rule would not have changed. EPA did this, for example, by responding to Sierra Club’s recommendations for changes in estimated oil prices and nuclear capacity. EPA’s findings and conclusions after adopting Sierra Club’s assumptions for future oil prices and nuclear capacity are detailed below. The most critical assumptions Sierra Club still objects to are those concerning utility behavior which incorporate what it terms a “perverse hypothesis” that less stringent controls can result in lower total emissions. EPA answered that charge by explaining why variable control could promise equivalent or better reduction of emissions than the stricter full control option:

One finding that has been clearly demonstrated by the two years of analysis is that lower emission standards on new plants do not necessarily result in lower national S02 emissions when total emissions from the entire utility system are considered. There are two reasons for this finding. First, the lowest emissions tend to result from strategies that encourage the construction of new coal capacity. This capacity, almost regardless of the alternative analyzed, will be less polluting than the existing coal- or oil-fired capacity that it replaces. Second, the higher cost of operating the new capacity (due to higher pollution costs) may cause the newer, cleaner plants to be utilized less than they would be under a less stringent alternative. These situations are demonstrated by the analyses presented here.

The crucial assumption leading to these findings is that utilities are “cost minimizers.” The cost minimization assumption implies that when faced with a decision the utility will choose the low-cost option, if risks between the options are neutral. Under the cost minimization model the higher the costs of pollution controls required by the NSPS, the more utilities will delay the retirement of older plants which do not have to comply with the NSPS, and the more utilities will be discouraged from building and operating new plants which must meet the NSPS. Since uniform control is costlier than variable control, uniform control is expected to result in greater reliance on old plants and less utilization of new plants than will variable control, which in turn leads to higher emissions. We see no basis for concluding that the adoption of this assumption about utility preferences constituted a clear error of judgment; indeed we are hard pressed to conjure up an alternative assumption about utility behavior that could be put into the computer model.

(b) The Reasonableness of EPA’s Conclusions

(1) The Reasonableness of EPA’s Conclusion That Variable Control Reflects a Better Balance of the Section 111 Factors Than Uniform Control

According to EPA, the variable standard strikes the proper balance between environmental, economic, and energy considerations, whether or not wet scrubbing or dry scrubbing technology is used. We agree because the findings of EPA’s regulatory analysis made under the assumption that wet scrubbing technology would be utilized, listed in Tables 2 through 5 from the preamble to the final rule (shown as Figures 5 through 8 in the appendix to this opinion), show clear advantages for adoption of the variable control option over the full control option favored by Sierra Club — apart from any considerations as to the use or savings emanating from the emergent dry scrubbing technology.

Table 2 details EPA’s projections for the national levels of sulfur dioxide emissions in 1995. The expected total national emissions for wet scrubbing under both variable control and full control are the same — approximately 20.6 million tons. However, Table 2 reveals that variable control achieves this level of emission with greater utility plant capacity burning more coal, while at the same time generating less sludge. The total projected capacity of plants burning coal in 1995 is 533 GW for the variable control option and 521 GW for the full control option. Wet scrubbing at levels permitted by variable control will result in only 50 million tons of sludge while full control is predicted to generate 55 million tons.

Table 3 details projections of 1995 regional sulfur dioxide emissions. A comparison of the figures listed in Table 3 for wet scrubbing at the variable control and full control levels indicates that there are tradeoffs of the different regional impacts of the two standards. The figures show that the East is better off under variable control while the West is better off under full control. With variable control the East will have 300,000 tons less emissions than under full control, but variable control will allow 200,000 tons more emissions in the West than would be experienced with full control in the West. The other two regions — the Midwest and West South Central — can expect roughly the same levels of emissions under either level of control.

Table 4 illustrates the effect of the proposed standards on 1995 coal production, western coal shipped East, and oil consumption by utilities. With regard to these energy impacts the comparative performance of variable control and full control is mixed. National coal production is expected to triple regardless of the level of the percentage reduction standard, from 647 million tons in 1975 to almost 1800 million tons by 1995. Although more western coal will be shipped East under variable control than under full control, 71 million tons versus 59 million tons, both levels of control will result in much lower shipments of coal eastward than the 122 million tons expected under the former standards. In addition, the local production of coal in the East will be slightly greater under variable control than under full control, 470 million tons versus 463 million tons, despite the fact that variable control will result in greater shipments of western coal to the East. Finally, variable control is estimated to involve consumption of 200,000 fewer barrels per day of oil than will full control.

Table 5 shows the expected economic impacts in 1995. Since, as has been noted, the model estimates greater plant capacity under variable control than under full control, the cost of this extra capacity makes the cumulative utility capital expenditures 6 billion dollars higher under variable control than under full control.

Capital expenditures are, however, only part of the overall cost under alternative standards. Annualized cost, for example, includes capital charges, fuel costs, and operation and maintenance costs associated with utility equipment — including pollution control equipment. Table 5 lists annualized cost under different standards as increments over the cost which could be expected under the former standard. EPA projects that despite the greater capital costs, the annual cost of variable control will be half a billion dollars less than the annual cost of full control. In other words, variable control is expected to cost 3.6 billion dollars a year more than the former standard, while full control will cost 4.1 billion dollars a year more than the former standard.

Table 5’s figures also demonstrate that variable control is more cost effective than full control. One measure of cost effectiveness is the incremental cost per ton of sulfur dioxide removal. The stated figures for the incremental cost per ton of sulfur dioxide removal are obtained by dividing the expected increase in annual cost by the expected decrease in emissions, as compared to the projected cost and emissions for the former standard. Since both variable control and full control should reduce emissions by 3.1 million tons, variable control is more cost effective than full control because the increased annual cost of variable control is 3.6 billion dollars while the increased annual cost of full control is 4.1 billion dollars, or half a billion dollars more. The incremental cost of sulfur dioxide removal, which is the ratio of the cost figures over the 3.1 million tons of increased emission reduction, is 1,161 dollars/ton for variable control and 1,323 dollars/ton for full control.

Finally, EPA’s analysis of wet scrubbing predicted that consumers would incur both lower direct costs (in the form of monthly residential energy bills) and lower indirect costs (reflecting price increases due to higher energy costs) under variable control as opposed to full control.

Results of subsequent selective modeling conducted after the publication of the final NSPS during the pendency of the petitions for reconsideration do not contradict the earlier results discussed above (the results are listed in tables shown as Figures 9 through 11 in the appendix to this opinion). Sierra Club’s petition for reconsideration criticized EPA’s econometric model because the assumed future oil prices were too low and the assumed growth rate of nuclear power plants was too high. To evaluate the petition EPA reran the computer model, performing what the agency called two “sensitivity tests.” These sensitivity tests first assumed higher oil prices and then assumed both higher oil prices and a lower nuclear growth rate, while holding the other modeling assumptions constant. Sierra Club claims “that when EPA ran the model . . . with more realistic assumptions concerning oil prices and nuclear power growth, full control showed lower total emissions [than variable control].” (Emphasis in original.) But we find that the results of the rerun analysis are entirely consistent with the adoption of a variable standard. The first sensitivity test which assumed only higher oil prices produced no significant changes in the relative advantages of the alternative control options, and both sensitivity tests indicated that variable control was the most attractive option. Even though the sensitivity test which assumed both higher oil prices and lower nuclear capacity showed, for the first time during the modeling analysis, that full control would produce lower national emissions than variable control, the difference in total emissions between the two options was only 100.000 tons. “[T]he cost of this additional 100.000 tons of control was estimated at $1.8 billion, which represents more than a 40 percent increase in the . . . cost.” EPA further explained:

The principal environmental benefit of full control [assuming both higher oil prices and lower nuclear capacity] would be felt in the West and West South Central. Through case-by-case new source review ample authority exists [under the Clean Air Act] to require more stringent controls as necessary to protect our pristine areas and national parks. ... As a result, the Administrator continues to believe that the flexibility offered by the variable standard will lead to the best balance of energy, environmental, and economic impacts....

For these reasons we do not believe that the post-promulgation modeling analysis provides convincing evidence that full control is preferable to variable control.

In sum, the results of EPA’s econometric modeling which forecast substantial benefits to be obtained by adopting the variable standard, provide adequate support for EPA’s decision to select that course on the basis of the environmental, energy, and cost factors specified in section 111.

(2) The Reasonableness of EPA’s Conclusion That Variable Control Promotes the Policies of the Act

The results of EPA’s regulatory analysis also persuade us that the variable standard does indeed advance policies of the Act other than those specifically incorporated in section 111.

First, variable control is not — as Sierra Club alleges — inconsistent with the purposes underlying the Act’s programs for the prevention of significant deterioration of air quality, and the provisions for eliminating the impairment of visibility in certain designated areas. Specifically, because EPA predicts that variable control will produce equivalent or lower total emissions of sulfur dioxide than any other control option, variable control protects air quality and visibility at least as well as any other standard. Regionally, all the control options produce about the same emissions in the Midwest and West South Central regions. Although variable control might result in higher annual emissions in the West than would be expected under full control, full control might yield even a greater increment of air pollution in the East. We agree that “it would not have been a reasonable exercise of discretion to impose additional costs of over a billion dollars per year merely in order to transfer several hundred thousand tons of sulfur dioxide annually from the West to the East.” Nonetheless, we are not insensitive to possible regional hardships and do not mean to imply that they may be ignored. The NSPS, as EPA recognizes, are only a minimum national standard, and there are other mechanisms provided in the Clean Air Act which should be activated in appropriate circumstances to protect troubled areas.

Second, the findings also support EPA’s determination that variable control serves what the parties agree are the relevant purposes of section 111, which the legislative history says must be accommodated whenever EPA chooses to vary the percentage reduction standard.' For example, the competitive advantage previously enjoyed by some states under former standards will be eased, since all new coal-fired sources are subject to the same emissions ceiling and all must apply some level of continuous emission reduction technology to control sulfur dioxide emissions. Consequently the standards assist in eliminating the advantage of using only low sulfur coal throughout the country or of relocating to areas where scrubbing was not previously required because low sulfur coal was available locally. The advantage of the lower percentage reduction requirement available to plants burning low sulfur coal is offset to a degree by countervailing considerations, such as the costs of mining, transportation, and relocation, competition for supply, and state regulations.

Other purposes of section 111 also appear to be well served. One highlighted in the Conference Committee Report was “maximizing the use of locally available fuels.” EPA found that the 70 percent minimum floor was “sufficiently stringent to reduce the amount of low-sulfur coal that moves eastward when compared to the [former] standard. Admittedly, a uniform 90 percent requirement would reduce such movements further, but . . . such gains would be of marginal value when compared to expected increases in high-sulfur coal production.” EPA’s figures show that 59 million tons of low sulfur coal would be shipped East under full control while 71 million tons would be shipped East under variable control. In light of the projected increase in coal production, from 647 million tons in 1975 to close to 1800 million tons in 1995 we find no abuse of discretion in EPA’s determination that the additional 12 million tons projected to be shipped East under variable control would not significantly interfere with the use of locally available coal. We are not especially troubled by Sierra Club’s concern that under variable control, utilities in the Midwest “can choose between burning local high-sulfur or imported Western low-sulfur coal.” Added flexibility is an attractive feature of variable control for many reasons, and among other things, will promote a more “balanced coal demand within the utility sector.” In addition, we are informed by Intervenor MAMU that variable control will increase the propensity of some midwestern utilities to use local coal rather than to import low sulfur coal from the West.

The combination of stringency and flexibility afforded by variable control satisfies still another stated purpose of section 111: freeing low sulfur coal for use in existing plants where it is harder to control emissions and where low sulfur fuel is needed to achieve compliance. The expected increase in the production of all types of coal, by itself, would probably provide sufficient supplies of low sulfur coal to existing “dirty” plants. Under variable control, however, these older plants should be retired at a more rapid rate than under full control. Thus, as low sulfur coal supplies grow, the demand from older plants should decline. Variable control should also reduce the number of long distance shipments of low sulfur coal to newer plants since some scrubbing will be required whatever kind of coal is used. It will become just as economical for some utilities, like the midwestern plants noted above, to burn higher sulfur content local coal, rather than to consume more distant low sulfur coal.

Overall, we must conclude that EPA’s rationale for the variable standard— completely apart from dry scrubbing — is supported by the agency’s findings, and that the agency’s rationale demonstrates that the variable standard satisfies both the language of section 111 and the policies enumerated in its legislative history.

C. The Dry Scrubbing Controversy

Notwithstanding the reasons proffered by EPA for adopting the variable standard under the assumption that utilities would use wet scrubbing technology, Sierra Club argues that EPA’s findings and conclusions about the emergent dry scrubbing technology are actually the cornerstone of the agency’s rationale for the variable standard. For this reason, Sierra Club maintains, the variable standard must be set aside because: (1) EPA is not authorized by section 111 to consider the impact of the NSPS on the development of a new technology like dry scrubbing and (2) EPA’s determinations about the efficiency of dry scrubbing technology, and the means of encouraging its development, are not supported by the record.

We address these arguments because EPA’s published rationale for the variable standard attests to the important role dry scrubbing technology played in the evolution of the rule. As we have shown, EPA’s justification for the rule in terms of statutory criteria does not depend on dry scrubbing technology. However, the agency’s explanation of the evolution of the standard indicates that the impetus for EPA’s examination of the 70 to 90 percent control option in the post-comment period phase three analysis stemmed from the agency’s desire to reexamine the potential of dry scrubbing. According to EPA’s rationale the development of dry scrubbing technology was perceived as a major bonus of promulgating the variable standard. We conclude that EPA’s consideration of dry scrubbing as a reason for its selection of a nonuniform standard is consistent with the agency’s authority under section 111, and that there is support in the record for doing so. In a final section we review the procedural objections that Sierra Club raises to EPA’s consideration of dry scrubbing.

1. The Role of Dry Scrubbing Technology in EPA’s Rationale for the Variable Standard

In the preamble accompanying the proposed NSPS, EPA referred only in passing to dry scrubbing. Dry scrubbing was described as one of several new and promising “emerging technologies” with considerable “potential” but not yet sufficiently demonstrated to be a basis for the proposed standard. The background documents to the proposal also gave limited attention to dry scrubbing. The proposed standard was clearly based on the level of emission control achievable by wet scrubbing systerns, although EPA noted that “the use of other systems should not be discouraged. In this regard, a number of emerging technologies show promise.”

When the results of the phase two analysis were published in December 1978 EPA did not mention dry scrubbing at all. By that time EPA had received some comments from advocates of dry scrubbing and at the public hearing held that month testimony was given favoring a 70 percent floor on the percentage reduction standard so as not to preclude the use of dry scrubbers.

Dry scrubbing was first incorporated into EPA’s regulatory analysis in phase three — ■ conducted after the close of the comment period. In the preamble to the final rule EPA explained that phase three modeling introduced:

the incorporation of dry SO2 scrubbing systems. Dry scrubbers were assumed to be available for new and retrofit applications. The costs of the systems were estimated . . . based on pilot plant studies and contract prices for systems currently under construction. Based on economic analysis, the use of dry scrubbers was assumed for low-sulfur coal [less than 3 lbs./MBtu] applications in which the control requirement was 70 percent or less. For higher sulfur content coals wet scrubbers were assumed to be more economical.

The results of the phase three analysis showed that variable control was preferable to uniform control under the wet scrubbing assumption, and to an even greater extent under the dry scrubbing assumption. (The results are listed in Figures 5-8 in the appendix to this opinion.)

These findings of the phase three regulatory analysis were published in June 1979 when the final rule was announced. The preamble to the final rule, in contrast to the agency’s statement at the time of the proposal and after phase two, is replete with references to both wet scrubbing and dry scrubbing. The preamble reveals that both pollution control technologies played a role in EPA’s decision. For example, EPA stated:

Although the standards are based on [wet] lime or limestone FGD systems, other commercially available [wet] FGD systems . . . are also capable of achieving the final standard. In addition, when specifying the form of the final standards, the Administrator considered the potential of dry S02 control systems. . . .

(Emphasis supplied.)

EPA’s rationale for the final NSPS notes that the critical issue of variable control “was made more complex by the emergence of dry SO2 control systems.” EPA claimed that “[a]s a result of public comments on the discussion of dry S02 technology in the [September 1978] proposal, the EPA staff examined the potential of this technology in greater detail.” EPA explained that it found dry scrubbing to be “progressing rapidly” as an attractive alternative to wet scrubbing but that the applicability of dry scrubbing was limited to low sulfur coal.

EPA’s rationale continued:

Faced with these findings, the Administrator had to determine what effect the structure of the final regulation would have on the continuing development and application of this technology. A thorough engineering review of the available data indicated that a requirement of 90 percent reduction in potential SO2 emissions would be likely to constrain the full development of this technology by limiting its potential applicability to high alkaline content, low-sulfur coals. For non-alkaline, low-sulphur coals, the certainty of economically achieving a 90 percent reduction level is markedly reduced.
In the face of this finding, it would be unlikely that the technology would be vigorously pursued for these low alkaline fuels which comprise approximately one half of the Nation’s low-sulfur coal reserves. In view of this, the Administrator sought a percentage reduction requirement that would provide an opportunity for dry S02 technology to be developed for all low-sulfur coal reserves and yet would be sufficiently stringent to assure that the technology was developed to its fullest potential. The Administrator concluded that a variable control approach with a minimum requirement of 70 percent reduction potential in S02 emissions (30-day rolling average) for low sulfur coals would fulfill this objective.
In addition to promoting the development of dry SO2 systems, a variable approach offers several other advantages often cited by the utility industry [advantages listed] .... While these points alone would not be sufficient to warrant adoption of a variable standard, they do serve to supplement the benefits associated with permitting the use of dry scrubbing.

(Emphasis supplied.)

Sierra Club insists that this statement amounts to a concession that the agency’s justification for variable control hinges on dry scrubbing and urges the following interpretation of the above-quoted language:

In the final rule-making the agency conceded that, based only on a consideration of wet scrubbing techniques, a deviation from uniform control should not have been adopted, and that any supposed advantages for partial controls “alone would not be sufficient to warrant adoption of a variable standard.

We do not believe, however, that a fair reading of the passage supports Sierra Club’s interpretation. Rather the language indicates only that the incidental benefits of variable control, at the micro or plant level “alone would not be sufficient to warrant adoption of a variable standard” without regard to the macro or national level economic, environmental, and energy considerations required by section 111 of the Act. Thus read, it is by no means a concession that the regulatory analysis of the alternative wet scrubbing scenario does not support variable control, but only an enumeration of the “supplemental [plant level] benefits associated with permitting the use of dry scrubbing.”

In fact, EPA’s rationale carefully distinguishes between the macro level considerations supporting variable control and the additional advantages of developing dry scrubbing:

By fashioning the SO2 standard in this manner, the Administrator believes he has satisfied both the statutory language of section 111 and the pertinent part of the Conference Report. The standard reflects a balance in environmental, economic, and energy considerations by being sufficiently stringent to bring about substantial reductions in SO2 emissions . . . yet does so at reasonable costs without significant energy penalties. When compared to a uniform 90 percent reduction, the standard achieves the same emission reductions at the national level. More importantly, by providing an opportunity for full development of dry S02 technology the standard offers potential for further emission reductions ..., cost savings . . ., and a reduction in oil consumption . . . when compared to a uniform standard.

(Emphasis supplied.)

Our own reading of EPA’s rationale convinces us that although dry scrubbing is not relied on as the exclusive or even primary justification for the variable standard, the agency’s consideration of dry scrubbing did influence the course of the rulemaking by suggesting the 70 percent figure for a variable control standard that was tested and ultimately adopted. We have little doubt, based on a thorough reading of the record, that if EPA had never brought dry scrubbing to the forefront in the later stages of the rulemaking, the agency might still have selected and successfully defended the reasonableness of the variable standard. However, that is not what occurred here. Consequently our review of the standard turns to the question of whether it was legitimate under section 111 for EPA to take account of dry scrubbing in the way it did.

2. The Legitimacy of Considering Emerging Technology in Setting Section 111 Standards

Sierra Club strongly argues that EPA had no business worrying about emerging technology because section 111 does not explicitly include “technological innovation” as one of the factors EPA is to balance along with considerations of cost, energy and nonair health and environmental impacts. In fact, Sierra Club argues, Congress enacted a separate and exclusive provision, section lll(j), to deal with the subject of technological innovation. Section lll(j) authorizes EPA to encourage new technology through the grant of waivers from the NSPS to those sources of emissions planning to use “an innovative technological system or systems of continuous emission reduction.”

We do not believe that EPA is precluded from encouraging technological innovation through the NSPS either because section 111(a) prohibits the agency from doing so or because section lll(j) is meant to be the exclusive statutory mechanism for promoting new methods of pollution control.

Our interpretation of section 111(a) is that the mandated balancing of cost, energy, and nonair quality health and environmental factors embraces consideration of technological innovation as part of that balance. The statutory factors which EPA must weigh are broadly defined and include within their ambit subfactors such as technological innovation.

We have no reason to believe Congress meant to foreclose in section 111(a) any consideration by EPA of the stimulation of technologies that promise significant cost, energy, nonair health and environmental benefits. Our view is consistent with legislative history, which reveals Congress’ concerns that the NSPS should not stymie technological innovation. So long as EPA considers innovative technologies in terms of their prospective economic, energy, nonair health and environmental impacts the agency is within the scope of its authorized analysis. This is not to say, however, that NSPS may be relaxed just to accommodate an uncertain and unproven technology. Rather, when balancing the enumerated factors to determine the basic standard it is appropriate to consider which level of required control will encourage or preclude development of a technology that promises significant advantages with respect to those concerns.

According to our reading, section lll(j) supplements rather than restricts EPA’s discretion under section 111(a) to encourage innovative technology. Section lll(j) specifies the circumstances in which EPA may grant waivers from NSPS to individual plants using innovative technology which has not been adequately demonstrated and which will inter alia :

achieve greater continuous emission reduction than that required to be achieved under the standards of performance which would otherwise apply, or achieve at least an equivalent reduction at lower cost in terms of energy, economic, or non-air quality environmental impact. . . ,

In our view, a symbiotic rather than mutually exclusive relationship exists between the NSPS of section 111(a) and the technology waivers of section lll(j). Section lll(j) waivers are limited to individual plant situations where the technology is capable of eventually achieving a level of emissions reduction which is equal to or greater than that specified in the section 111(a) NSPS. Thus, the ability to grant section lll(j) waivers would be unduly restricted or entirely foreclosed if the NSPS were set too high. If Congress intended any substantial use of lll(j) waivers, as we presume that it did, it is only plausible that Congress also meant for emerging technologies to be given consideration when EPA promulgated NSPS.

The Act does not state that section lll(j) is the exclusive provision for dealing with technological innovation. Elsewhere in the Act, however, Congress has explicitly indicated when EPA’s discretion to work toward a particular end is limited to the confines of a specific provision. Absent such language in section lll(j), we hesitate to say that EPA is limited to the narrow terms of this section in dealing with the important area of new and developing technologies, particularly in situations where section 1110) waivers to individual plants would not provide sufficient incentives to spread new technology throughout the industry.

In short, we can find no statutory bar to EPA’s consideration of how various NSPS options will affect the development of new technologies which have economic, energy, and environmental implications of their own.

3. The Adequacy of the Record for Dry Scrubbing’s Role in EPA’s Rationale

EPA has explained that its evaluation of the technical capabilities and commercial attractiveness of dry scrubbers precipitated the decision to test the 70 percent floor option, and its desire to encourage the development of dry scrubbing reinforced the agency’s preference for the variable standard. We now proceed to examine whether there is a reasonable basis in the record for the agency’s conclusions about the appropriate level of control in light of the potential of dry scrubbers.

We note that the nature of our inquiry here is different from that required had EPA relied on dry scrubbing as adequately demonstrated technology and found that the variable standard was the best level of control — in light of the relevant considerations — achievable by dry scrubbing. Here the variable standard was chosen as the best level of control achievable by wet scrubbing, admittedly an adequately demonstrated technology.

We also do not confront the situation where EPA has set a standard at a particular level believed necessary to promote a new technology, even though the agency’s regulatory analysis demonstrated that another level of control was optimal, after considering all relevant factors apart from the new technology. In such a case our close scrutiny of the factual basis for the standard would involve a balance: we would have to weigh the magnitude of the standard’s departure from the level of control otherwise indicated by the agency’s regulatory analysis against the weight of the support in the record that substantial benefits would eventually accrue from adjusting the standard on the basis of the new technology. The greater the imprint of the new technology on the final rule, the more demanding our review of the evidence about the potential benefits and capabilities of new technology. By the very nature of its newness, it would be inevitably harder for EPA to acquire as precise and complete information about the emerging technology as would be available in the case of older, more established technologies. Thus the difficulty of justifying a standard that diverges from a level determined by weighing cost, energy, and environmental effects of the best presently demonstrated technology, solely to account for new technology, should provide built-in safeguards against overuse of such a justification and prevent circumvention of the primary statutory goals.

The present situation does not present such a risk because the control level EPA believed was necessary to promote dry scrubbing was found to be optimal even aside from dry scrubbing considerations. This circumstance obviates the need to determine whether EPA’s conclusions about dry scrubbing can be relied upon as an independent basis for the variable standard. We do require, however, that the record substantiate the reasonableness of EPA’s preliminary step of turning to a standard with a 70 percent floor for the purpose of comparing its potential impacts with other control options, and basing its subsequent adoption of that 70 percent standard, even partially, on the prospects of encouraging development of dry scrubbing.

Sierra Club’s quarrel in this regard is not with EPA’s judgment that 70 percent removal on low sulfur coal is technologically and economically feasible for dry scrubbers. On the contrary, as Sierra Club argues in advocating a higher standard, the record contains considerable evidence which indicates that dry scrubbing can achieve significantly better than the 70 percent floor adopted by EPA. EPA itself announced in the proposed NSPS that dry scrubbing appeared capable of eventually matching the performance of wet scrubbing.

Sierra Club does object, however, to EPA’s conclusion that the 70 percent standard is necessary to encourage utilities to use dry scrubbers. Much of the record evidence concerning whether it is appropriate to set the minimum standard at 70 percent in order to promote the development of dry scrubbing technology revolves around the assertion that dry scrubbing low alkaline coal is more expensive than dry scrubbing high alkaline coal because of “uncertainty in the stoichiometric ratio” required to achieve a 70 percent reduction for nonalkaline coals.

Sierra Club’s response is that the “alkaline” issue is a red herring. EPA’s concern over “uncertainty in the stoichiometric ratio” means only — according to Sierra Club — that EPA does not know precisely how much more additional lime will have to be added to a dry scrubber system when the natural alkalinity of the coal is too low to obtain the necessary results in the sulfur dioxide removal process. However, the need to add reagent to low alkaline coal is not unique to dry scrubbing — lime or limestone reagents are frequently required in wet scrubbing systems burning low alkaline coal.

The implications of the “uncertainty in the stoichiometric ratio” are thus principally financial. If the cost of the extra lime injected into the dry scrubber is too high, presumably it will make the system economically unattractive for removal efficiencies greater than 70 percent. We have examined the source materials containing the economic analysis offered in support of this conclusion, and find only limited substantiation for the perception that 70 percent removal efficiency is the limit of economical dry scrubber performance, or that the extra cost of scrubbing low alkali coal would tend to make dry scrubbing economically less attractive than wet scrubbing at a higher than 70 percent level.

There is, however, other evidence in the record concerning EPA’s prediction that utilities will refrain from dry scrubbing if the minimum standard is higher than 70 percent or conversely be enticed to use them if the standard drops to 70 percent. Witnesses at the December 1978 hearing voiced a preference for relaxing the percentage reduction standard on the basis that it would encourage dry scrubbing. Two comments received by EPA proposed 70 percent as the preferred level of control for that purpose. The Electric Utilities, as the spokesman of the industry, also submitted comments which emphasized that a standard higher than 70 percent would inhibit utilities from trying dry scrubbing since they would perceive no advantage in using an emerging and still risky technology over a demonstrated one like wet scrubbing. This view in turn must be considered in light of other evidence that several plants have in fact opted for dry scrubbing for performance levels greater than 70 percent, while still other utilities operating at the 70 percent level are choosing wet scrubbers. Overall EPA has projected that most new plants would, in fact, install wet scrubbers.

In sum, the support in the record for selecting 70 percent as the magic percentage for encouragement of dry scrubbing is less than overwhelming. However, three things do stand out on the record. First, dry scrubbing has significant potential as a cheaper, energy conserving, and environmentally sound alternative to wet scrubbing. Second, despite the considerable potential advantages of dry scrubbing systems over wet scrubbing systems, dry scrubbing is not yet a proven or “adequately demonstrated” technology and its future is uncertain. Third, all of the testing of dry scrubbing performance has been done on high alkaline coal, while low alkaline coal makes up 50 percent of national coal reserves and 90 percent of the low sulfur coal reserves in the West.

On the basis of this evidence we find it was reasonable for EPA to seek to encourage dry scrubbing and to be concerned with the effect of the NSPS on the future of the new technology. Furthermore, on the basis of the entire record it was not unreasonable for EPA to believe that the leeway afforded by the variable standard from the requirements of the stricter 90 percent reduction requirements would promote dry scrubbing. Given the state of this record we would have been reluctant to uphold EPA’s discretion to vary the standard solely on the basis of dry scrubbing, but we are satisfied that it was legitimate for EPA to find that variable control with a 70 percent floor was an option that would be worthwhile to further examine in terms of its national and regional impacts under alternative wet scrubbing and dry scrubbing assumptions.

To put our conclusion upholding the 70 percent standard in further perspective: the 70 percent minimum level of emission control is permissible only when the overall emission level is reduced from 1.2 lbs./MBtu to .60 lbs./MBtu. Therefore, it cannot be contended that the new NSPS are more lax than the former NSPS, but only that when a plant halves its total emissions, then the percentage reduction standard does not independently require a uniformly high percentage reduction at all times — regardless of the sulfur content of the coal burned or other policy considerations such as fostering the availability of cheaper, cleaner, energy saving technologies.

We now complete our review of the variable standard by considering whether the substantively acceptable standard was procedurally defective.

D. The Adequacy of Notice and the Opportunity to Comment on the Rationale for the Variable Standard

Sierra Club complains that EPA’s focus on dry scrubbing and the determinative phase three regulatory analysis came only after the public comment period closed in January 1979; hence, interested parties in the rulemaking were not informed of these developments in time to make meaningful comments before the final rule issued in June 1979. Sierra Club argued in its petition for reconsideration that a new proposal should have been resubmitted for public comment at the point that EPA seriously began to consider the variable standard ultimately adopted.

The procedural requirements for notice and comment applicable to this case are specified in section 307(d) of the Act, which is discussed below in our review of EDF’s appeal of the 1.2 lbs./MBtu emission ceiling. For now it suffices to state that section 307(d) provides for published notice of a rulemaking to be accompanied by a statement of its basis and purpose which includes (a) the factual data on which it is based, (b) the methodology used in obtaining and analyzing the data, and (c) the major legal and policy considerations underlying the rule. All documents which become available after the proposed rule has been promulgated which are “of central relevance to the outcome of the rule” must be entered into the docket, and the agency must allow enough time for participants in the rulemaking to respond to those documents with comments. However, these provisions do not require EPA to select a final rule from among the precise proposals under consideration during the comment period. Rather, incremental changes are permissible so long as the final rule is a “logical outgrowth” of the proposals highlighted and discussed during the notice and comment period. It is entirely proper and often necessary for the agency to continue its deliberations and internal decision-making process after the close of public comment in order to assimilate those comments and arrive at a policy choice. Our decision here involves a question of degree: whether a sliding scale 70-90 percent reduction requirement is a logical outgrowth from the numerous alternative options discussed by EPA in its September 1978 proposal and in the December 1978 interim announcement. In addition we must decide if EPA’s late consideration of dry scrubbing was such a detour from the course of the rulemaking that in fairness to the public and interested parties the agency should be required to retrace its steps, give notice of its new focus, and reopen the comment period.

EPA, of course, denies the existence of any procedural irregularity in the promulgation of the variable standard. When the agency denied Sierra Club’s petition for reconsideration it stated that the notion that “the phase 3 analysis was a new venture” was “false.” According to EPA, phase three featured no new modeling concepts or input assumptions, only “refinements” of earlier analysis. EPA insists that the 70 percent level of control which was introduced in order to consider the impact of dry scrubbing, raises basically the same policy issues as all the percentage reduction options previously analyzed.

While we find that Sierra Club’s criticism of the procedural history of the variable standard is not unwarranted, we conclude that there was sufficient notice and comment on matters which are “of central relevance” to support EPA’s rationale for the variable standard. It is indeed true that the 70 percent level of control did not surface as a serious contender until after the final bell sounded in the public arena, and many of the supporting documents related to dry scrubbing were inserted into the record in a last round flurry of agency activity. Yet it is important to evaluate EPA’s ultimate selection of 70 percent as the floor for the standard in the context of the agency’s decision to adopt some form of non-uniform sliding scale standard. There can be no doubt that the latter decision benefited from ample notice and comment. EPA stated at the time of the proposal that it might adopt a variable percentage reduction standard as opposed to the proposed 85 percent uniform standard, and emphasized that “[t]he principal issue associated with this proposal is whether electric steam generating units firing low-sulfur content coal should be required to achieve the same percentage reduction in potential SO2 emissions as those burning higher sulfur content coal.” The preamble to the proposed rule continued:

Resolving this question of full versus partial control is difficult because of the significant environmental, energy, and economic implications associated with each alternative. The Administrator has not made a final decision on which of the alternatives should be adopted in the final standard and solicits additional data on these impacts before promulgating the final regulations.

(Emphasis supplied.) Throughout the rule-making period from December 1977 until February 1980, extensive public comment centered on the issue of whether the percentage reduction should be uniformly applied.

The possibility of adopting a “sliding scale” standard varying with the sulfur content of coal was also discussed during and after the comment period. EPA considered several sliding scale options in terms of their economic, energy, and environmental impacts. These options included two sliding scales with maximum control at 85 percent, one of these with minimum control at the 20 percent level initially favored by the Electric Utilities and the other with minimum control at the 33 percent favored by the Department of Energy. In addition, EPA analyzed a 20 to 82 percent sliding scale and two options with a uniform 90 percent requirement in the West and sliding scales in the East (33 to 90 percent and 50 to 90 percent). After the close of the public comment period, EPA evaluated the 70 to 90 percent alternative and published the results under both wet and dry scrubbing assumptions. Finally, after promulgation of the final rule EPA considered the sliding scale option at the 50 percent minimum level urged by the Electric Utilities in their petition for reconsideration.

The record also shows that the phase three analysis with a 70 percent minimum floor was a continuation of the type of regulatory analysis performed during phases one and two. Aside from adjustments in the model to account for the assumption that utilities would use dry scrubbers, there were no radical changes in the econometric model that tested the likely impacts of the 70 to 90 percent control option. The analytical format that EPA relied on in phase three was subject to broad review in phases one and two by both the public participants in the rulemaking and by the joint interagency working group. In fact, Sierra Club’s objections to the phase three modeling are virtually identical to the criticisms of the phases one and two modeling that Sierra Club registered with the agency. EPA repeatedly solicited comments on the model, and on at least two occasions it responded to public comment by adjusting the analysis.

The subject of dry scrubbing and the question of how the NSPS would affect emerging technology were not introduced for the first time in phase three. On the contrary, there was a discussion of these matters in December 1977 — well before EPA even proposed the NSPS — at a public hearing held by the National Air Pollution Control Techniques Advisory Committee (NAPCTAC). Both dry scrubbing and the concern for emergent technology were discussed (though not emphasized) by EPA in the preamble to the proposed rule and the background support and technical documents. The Electric Utilities filed initial comments in December 1978 and filed supplemental and reply comments in January 1979 which advocated varying the percentage reduction standard from the maximum feasible level of wet scrubbers in order to encourage new technologies like dry scrubbing. Individual utilities and local governmental agencies testified and filed comments which detailed the capabilities of dry scrubbers and the advantages of promoting the use of this technology. On the other hand, the comments filed jointly in January 1979 by EDF and the Natural Resources Defense Council (“NRDC”) opposed EPA’s statutory authority to adjust the NSPS to account for new technology like dry scrubbing. Sierra Club apparently did not comment on dry scrubbing or emerging technologies until after the final NSPS were promulgated.

The record further shows that the parties had actual notice before the final rule was published in June 1979 of EPA’s focus on the 70 to 90 percent variable standard and of its heightened interest in dry scrubbing. For example, on April 20, 1979, NRDC and EDF jointly wrote to EPA vigorously criticizing EPA’s “new rationale” for allowing a sliding scale standard with a 70 percent minimum removal requirement in order “to avoid stifling the development of certain new technologies, such as dry scrubbing.” The letter was docketed in the administrative record on May 2, 1980. The Electric Utilities’ letter of April 23, 1979 also discussed the 70 to 90 percent standard and the importance of dry scrubbers to EPA’s rationale for this alternative standard. Copies of this letter were sent to interested parties including Sierra Club, EDF, and NRDC.

Beginning in early 1979 and continuing until the publication of the final rule, EPA prepared and entered on the record several documents concerning dry scrubbing. These documents included EPA’s economic comparison of dry scrubbing with wet scrubbing, a memorandum on the technical capability of dry scrubbers, and material on recent developments in dry scrubbing technology. The preamble to the final rule and the supporting background document incorporated large portions of these late entries into their text.

Viewing this record as a whole, we conclude that a variable sliding scale percentage reduction requirement was generally understood to be a serious possibility from the start of the rulemaking and that the issue of whether the standard should accommodate emerging technologies was raised by public comments. We also find that there was information on the potential of dry scrubbers in the record from the beginning of the rulemaking, although this was generously supplemented at the last stages of the proceeding.

Nonetheless, since the record contains the alternative “wet scrubbing” justification for the variable standard, and since the parties knew about EPA’s growing interest in dry scrubbing, we cannot say that the failure to provide for more time to comment on the late entries into the dry scrubbing controversy is “so serious and related to matters of central relevance to the rule that there is a substantial likelihood that the rule would have been significantly changed if such errors had not been made.” Otherwise, we find that the 70 percent minimum level of control came within the scope of alternative standards previously considered which ranged from a 20 percent minimum to a 90 percent maximum, and was not so significant a departure from prior sliding scale proposals as to require a new public comment period.

This rulemaking was by no means a neat and tidy proceeding, and it might well have been the wiser course if EPA had chosen to publish a new proposal for another round of comment, but we cannot say that the absence of new notice and comment is a fatal defect. For these reasons we decline to remand the variable standard to EPA on the procedural grounds argued by Sierra Club.

III. THE 90 PERCENT REMOVAL STANDARD

The Electric Utilities attack the NSPS insofar as they require a 90 percent reduction in the potential sulfur dioxide emissions from the combustion of high sulfur coal (at least 6 lbs./MBtu) measured on a thirty day rolling average. EPA’s position is that the record demonstrates that the 90 percent standard is achievable even in the most difficult situations by the use of precombustion fuel preparation techniques such as physical coal cleaning (“PCC” or coal washing) followed by post-combustion wet scrubbing of flue gas (“FGD” or scrubbing). The Electric Utilities contend that when the 90 percent standard was promulgated it was based on the use of FGD alone and that it is procedurally improper . for EPA to rely on a post hoc rationale for the standard which depends on the combined use of FGD and coal washing. The Electric Utilities also say that the 90 percent standard is not adequately demonstrated to be achievable even if FGD and coal washing or any other technology are used together. They point to several alleged deficiencies in the record and in EPA’s statistical analysis to illustrate the lack of support for the agency’s conclusions about the achievability of the standard.

A. Notice as to the Basis of the 90 Percent Standard

The Electric Utilities argue that both the proposed and the final NSPS were based on the level of emission reduction achievable by the application of FGD technology alone. Then, when the Electric Utilities showed in their petition for reconsideration that the 90 percent standard was not achievable by scrubbing alone, they say EPA, in denying the petition, impermissibly redefined the basis for the standard to include a combination of coal washing and scrubbing. Alternatively, the Electric Utilities maintain that even if the final rule was based on combined technology, EPA violated the procedural provisions of the Act which require that the promulgated rule must be accompanied by an explanation of any major changes in the final rule from the proposed rule.

1. The Basis of the Final Standard

EPA steadfastly insists that the final standard was clearly based on the performance of scrubbing in conjunction with precombustion technologies like coal washing and admits that “[i]f the standard were based solely on FGD, it would probably not be achievable.” The Electric Utilities, EPA claims, are “trying to distract the Court from EPA’s analysis of the actual standard by erecting and destroying a straw man.” We do not believe that the Electric Utilities’ contention may be dismissed quite that easily.

It is undisputed that the proposed percentage reduction standard — a uniform 85 percent removal requirement measured on a 24 hour period — was based on the capability of “well designed, maintained and operated flue gas desulfurization systems” alone. The proposal specifically, albeit briefly, discussed and permitted a credit for fuel pretreatment such as coal washing to be counted toward meeting the 85 percent standard. EPA stated, however, that fuel pretreatment was not required to achieve the proposed standard.

In the preamble to the final rule, the technological basis for the 90 percent standard was less explicit:

Under section 111(a) of the Act, a standard of performance for a fossil-fuel-fired stationary source must reflect the degree of emission limitation and percentage reduction achievable through the application of the best technological system of continuous emission reduction taking into consideration cost and any nonair quality health and environmental impacts and energy requirements. In addition, credit may be given for any cleaning of the fuel, or reduction in pollutant characteristics of the fuel, after mining and prior to combustion.

At one point in the same preamble EPA conceded that for some high sulfur coals, the standard could only be achieved by combining scrubbing and coal washing:

Based on the public record and additional analyses performed, the Administrator concluded that a 90 percent reduction in potential S02 emissions (30-day rolling average) has been adequately demonstrated for high-sulfur coals. This level can be achieved at the individual plant level even under the most demanding conditions through the application of flue gas desulfurization (FGD) systems together with sulfur reductions achieved by currently practiced coal preparation techniques. Reductions achieved in the fly ash and bottom ash are also applicable.

But later in the same preamble EPA states:

SO2 Control Technology — The final SO2 standards are based on the performance of a properly designed, installed, operated and maintained FGD system. Although the standards are based on lime and limestone FGD systems, other commercially available FGD systems (e. g., WellmanLord, double alkali and magnesium oxide) are also capable of achieving the final standard.

The preamble also contains a discussion of the potential of physical coal cleaning. EPA stated that while it did not consider coal washing alone to be adequately demonstrated to achieve the standard, coal washing offered the following benefits when used in conjunction with FGD:

(1) the S02 concentrations entering the FGD system are lower and less variable than would occur without coal cleaning,
(2) percent removal credit is allowed toward complying with the S02 standard percent removal requirement, and (3) the S02 emission limit can be achieved when using coal having a sulfur content above that which would be needed when coal cleaning is not practiced.

We believe that these passages, when read together, can be construed reasonably to say that the standard did not envision achievement of the standard by scrubbing alone. Rather, at the time of promulgation EPA contemplated that in some cases where high sulfur coal would be burned it would be necessary to use pretreatment technologies as well. Thus, we cannot agree with the Electric Utilities that. EPA changed the basis for the standard seven months after the final rule on denial of the petition for reconsideration.

2. Notice That the Basis of the Standard Had Changed Since Proposal

The Electric Utilities also argue that the switch from a proposed standard based on FGD with optional credit for fuel pretreatment, to a final rule that is achievable only through the combined use of FGD and fuel pretreatment is a “major change” that, under the Act, requires an expanded and forthright explanation. Nonetheless we do not think that EPA’s ultimate dependence on fuel pretreatment to demonstrate the achievability of the standard in the “most demanding situations” came about without notice or that it actually prejudiced the Electric Utilities in any way that would require us to remand the standard for a new round of public comment.

From the beginning of the rulemaking EPA specified that credits for coal washing could be taken toward meeting the percentage reduction requirement. The technical and support documents for the proposed standard gave substantial attention to coal washing. For example, the record includes a February 1978 Interagency Report prepared for EPA by the Batelle Memorial Institute entitled “Physical Coal Cleaning for Utility Boiler SO2 Emission.” This report focused on the potential of PCC in implementing the proposed NSPS and specifically examined the combined use of FGD and PCC. The study concluded that the combination of coal washing plus FGD would be useful in meeting stricter standards (e. g., 0.4 lbs./MBtu ceiling as compared to 1.2 lbs./MBtu standard ultimately adopted) because “large quantities of high-sulfur coals cannot be cleaned to this level with FGD alone.” In fact, the Batelle Report concluded that “PCC may be useful in combination with other controls meeting this type of standard. PCC would allow the scrubber or other control system to operate at a lower efficiency since credit would be given for sulfur removal.”

EPA received several comments on the subject of sulfur removal by fuel pretreatment and on the combined use of coal washing and FGD. NRDC and EDF’s joint comments noted that there were numerous advantages to using FGD after coal washing such as the reduction of coal variability and sludge, and the lowering of shipping and maintenance costs. In addition, NRDC specifically recommended a standard based on the combined scrubbing-washing technologies. The Electric Utilities submitted comments that supported EPA’s position that coal washing alone could not be the basis for the NSPS but also objected to NRDC’s recommendation that the NSPS be based on both coal washing and FGD.

EPA targeted the importance of coal washing on at least two other occasions. With the agency’s December 1978 announcement of the phase two modeling results EPA stated that it had reassessed its modeling assumptions and had added coal washing to its analysis because “the coal washing credit ... was found to have a significant effect” on the modeling results. On April 5,1979 EPA held a meeting with the representatives of the coal industry, the Electric Utilities, and the environmental groups to discuss the state of the art of coal washing. Materials distributed at the meeting concerning coal washing were put into the record shortly thereafter.

Post-comment period submissions by the Electric Utilities, NCA, and EDF strongly suggest that the parties understood that the final standard was to be based on both FGD and fuel pretreatment. For example, the Electric Utilities’ March 2, 1979, comment criticized the “coal washing assumptions being relied upon to support the new more stringent standards purportedly being recommended” and stated that “the basis for the change [to a more stringent emissions ceiling and 90 percent reduction level] also appears to be the assumption that coal washing is universally applicable on high sulfur coals and that this will help resolve the additional difficulties inherent in scrubbing high sulfur coal.” Electric Utilities voiced its concern about EPA’s conclusion that “coal washing is an adequate basis on which to justify raising the maximum performance requirement from 85 percent monthly removal ... to 90 percent monthly removal.” Again on April 23, the Electric Utilities criticized EPA’s consideration of NSPS including a 90 percent requirement, because “the assumptions concerning demonstrated scrubber removal efficiency and coal washing underlying the staff proposal are not supported by the record. ...” Then on May 18, the Electric Utilities reiterated its opposition to EPA’s “assumption that scrubbers can routinely achieve 90 percent removal in high sulfur coal either alone or in combination with coal washing.” Having made this series of statements only a few months before promulgation of the standard the Electric Utilities cannot argue convincingly that they were unaware that the final rule might require FGD to be used with coal washing for high sulfur coals.

On this record, if EPA had plainly stated that the basis of the final rule had changed since the time of its proposal, there would be no question that the change would have been permissible. Indeed, section 307 of the Act by its very terms appears to anticipate that changes will take place during the course of the rulemaking. Despite the lack of a formal announcement, we find that the public had actual notice and an adequate explanation of the changes in the basis of the final rule. We believe that the parties were aware of the potential significance of coal washing to the justification for the final standard and that they were not prejudiced by a lack of opportunity to contest the agency’s conclusions about the capability of coal washing.

B. The Achievability of the 90 Percent Standard

EPA’s rationale for the achievability of the 90 percent standard is based on three determinations: First, that the long term median sulfur dioxide removal of 92 percent is achievable by the use of FGD alone. Second, that the variability in the performance of a well operated FGD system will not exceed 0.36. EPA calculates that when the 92 percent median is adjusted to account for the 0.36 FGD variability (as well as a so-called “autocorrelation factor”) FGD systems can achieve between 86 and 89 percent average efficiency. Third, EPA concluded that utilities with FGD systems »operating at these levels would be able to comply with the 90 percent removal requirement by employing other technologies for sulfur removal such as coal washing and ash retention.

The Electric Utilities challenge each element of EPA’s rationale for the 90 percent standard. The evidence on both sides is extraordinarily technical and often confusing. We have studied the record and the briefs with an eye toward judging whether, given the agency’s expertise in evaluating conflicting data and selecting among reasonable approaches for pursuing statutory goals, EPA has plotted a reasonable course through the evidentiary thicket and stated a logical rationale for the route it chose.

1. The Support For EPA’s Conclusions About FGD Performance

We begin with EPA’s finding that a 92 percent long term median reduction is necessary, along with a performance variability range of no greater than 0.36 standard deviation (at the 95th percent confidence level) to meet the 90 percent standard. The Electric Utilities are correct, and EPA concedes, that there is no data on the record showing that the 92 percent long term median figure is actually achieved on a continuous basis by any currently operating commercial lime or limestone system. However, EPA projects the 92 percent figure in part from: (1) data obtained from a very limited number of lime FGD systems that do perform for varying numbers of 24 hour periods (from 22 to 42) at medians of 88 and 89 percent, (2) other short term data from nonlime/limestone FGD systems that report efficiencies in excess of 90 percent, and (3) reference to “Japanese experience [which] shows that technology exists to obtain greater than 90 percent S02 removal.” Finally, EPA cites as a basis for its 90 percent standard the prediction that future plants can be designed and operated to improve on efficiency levels currently experienced throughout the industry.

The Electric Utilities say, on the other hand, that short term performances of less than 90 percent cannot be projected into a long term 92 percent median. Further, the short term data on performances of more than 90 percent is irrelevant because it is not taken from lime/limestone scrubbers cleaning high sulfur coal exhaust. They discredit the Japanese data because the conditions under which it was conducted are undocumented, and are indicative only of short term scrubbing of low to medium, rather than high sulfur coal. Further, the Electric Utilities profess no knowledge of the improved design features or operational practices that EPA relies on to predict future scrubbing achievability, and argue alternatively that many of EPA’s “improvements” have been already rejected by the industry as impractical or ineffective.

Even if the 92 percent figure were achievable, the Electric Utilities contend that EPA’s 0.36 variability range is not representative since it is based on data from only one plant. In addition, they are troubled by the fact that EPA did not include the autocorrelation factor in its statistical analysis until the Electric Utilities, in their petition for reconsideration, submitted their own analysis demonstrating the relevance of autocorrelation when determining whether a long term median will achieve a particular given level of control.

EPA responds that its most recent statistical analysis of scrubbing efficiency “is in close agreement with [the Electric Utilities’] analysis when the same process variation and amount of autocorrelation was assumed.” Although EPA’s analysis indicates that only 88 to 89 percent control (in a thirty day rolling average for a base loaded plant) and 86 to 87 percent control (in a thirty day rolling average for a peak loaded plant) are achievable, improvements in process variability can be expected to yield more than 89 percent minimum reduction by the use of FGD alone. These levels of performance, EPA argues, exceed the minimum FGD performance (85 percent) necessary to achieve total reduction of 90 percent when other precombustion technologies are used.

(a) The Achievability of 92 Percent Long Term Removal Efficiency

EPA states that “the most important measure of an FGD system ... is its median removal efficiency.” EPA determined originally that a 92 percent long term median removal was necessary to comply with the proposed 85 percent uniform standard measured on a 24 hour basis. At the time the final rule was promulgated it was not clear whether the 92 percent median performance was necessary to achieve the 90 percent standard based on the performance of both FGD and fuel pretreatment. However, in denying the Electric Utilities’ petition for reconsideration EPA explained that the 92 percent median removal by FGD was essential when combined with precombustion sulfur removal to achieve an overall 90 percent level of performance.

The 92 percent figure is derived from data on existing plants and on EPA’s projection regarding the capabilities of well designed and operated scrubbers in future plants. As EPA correctly points out, the NSPS apply only to new plants, and since most current FGD systems were not designed to operate at 90 percent removal efficiency, the NSPS should not be based solely on existing levels of removal efficiency. Nevertheless, to determine whether it was reasonable for EPA, even with expected improvements, to project a 92 percent median, we must first look at the agency’s test results at currently operating plants.

EPA’s test data show that long term removal efficiencies exceeding 92 percent occur on low sulfur coals both in this country and in Japan. Of course, this alone is insufficient to support the standard since the 90 percent standard applies to plants burning high sulfur coals and it is undisputed that high sulfur coals pose the greatest challenge for FGD processes.

EPA’s data also show that FGD systems using scrubbing reagents that are more reactive than lime or limestone were achieving very high sulfur removal efficiencies on a short term basis. For example, the magnesium oxide FGD at Philadelphia Electric’s Eddystone Station achieved a median sulfur dioxide removal of 96.8 percent in an 8 day test. The sodium based double-alkali FGD at Gulf Power Company’s Scholz Station achieved as high as 99 percent short term removal (we cannot determine from the record what the median performance was). Tests at the Wellman-Lord FGD unit at Northern Indiana Public Service Company’s Mitchell Station including a 41 day continuous period of operation, demonstrated 89.2 percent median removal for a total of fifty-six 24 hour periods.

The Electric Utilities argue and we are inclined to agree that this data is not conclusive since EPA specified that the standards were based on lime or limestone systems, and not the more expensive and less available regenerative systems, or systems using reagents and additives more reactive than lime. Both the proposed and the final standards, and the background support documents conclude that the standard is achievable by many types of FGD, including lime/limestone systems, Wellman-Lord, magnesium oxide, and double-alkali processes. However, EPA’s emphasis on the lime and limestone processes and the uncontested fact that the non-lime/limestone processes are not widely available, preclude EPA from demonstrating the achievability of the standard on the basis of data from non-lime and limestone scrubbers.

The data advanced by EPA from lime/limestone systems are sparse, primarily because few plants had any need to attempt to achieve removal efficiencies over 90 percent on high sulfur coal under the former standard. A lime system at Columbus and Southern Ohio Electric Company’s Conesville No. 5 plant burning high sulfur coal (4.5 to 4.9 percent) and designed for 90 percent removal attained a median of 88.8 percent. The data underlying that median, however, represents only 15 percent of a six month test period; the rest of the time the Conesville unit was malfunctioning. The only other data is from a pilot plant utilizing a lime system burning high sulfur (3.0 percent) coal at the Tennessee Valley Authority’s Shawnee Station. The Shawnee Station achieved an 88.6 median but the unit is only a 10 MW prototype plant.

EPA suggests that a 92 percent long term median removal may be interpolated between the lower 88.6 to 88.8 percent medians of the two lime scrubber units and the higher removal efficiencies of the non-lime Japanese and American units burning low sulfur coal. Counsel for EPA states that 92 percent represents “an intermediate level among the [FGD] data.” The Electric Utilities cast this reasoning in the worst, but not entirely unreasonable, light:

EPA counsel’s logic is truly remarkable: since one lime/limestone system can get 89 percent for an average of 24 out of 162 days and one regenerable system can get 96 percent for an average of 8 out of 22 days, then all future systems (lime/limestone and non lime/limestone) can get 92 percent long term mean remováis. On Sunday, September 21, George Brett of the Kansas City Royals had a .400 batting average. On that day, Eddie Murray of the Baltimore Orioles was batting .302. Given these facts, EPA counsel’s logic would lead to the conclusion that, in the future, all baseball players can be reasonably expected to bat .350.

(Emphasis in original, footnotes omitted.) We agree that splitting the difference between data for lime scrubbers treating high sulfur coal exhaust and the data for non-lime/limestone systems and systems treating low sulfur coal is an unacceptable method for demonstrating that a 92 percent median is achievable by a lime system burning high sulfur coal.

Thus we cannot accept EPA’s 92 percent median solely on the basis of evidence that only one commercial scale plant and one small pilot unit can almost but not quite meet the standard. To uphold the standard we must rely on EPA’s predictions that a 92 percent median can be achieved with some design and operational improvements in new scrubbers. Two reports in the record and the Supplemental Background Document for the NSPS elaborate in great detail the kind of changes in future scrubbers that could be expected to increase their performance. We have reviewed the materials and they appear to explain how the changes would improve FGD performance. The predictions in these documents are also supported to some extent by test results where use of a recommended improvement such as the addition of reactive agents to the lime slurry, actually increased removal efficiency above 92 percent over very short periods of time. In addition, we find it informative that the vendors of FGD equipment corroborate the achievability of the standard although their support for the standard, taken alone, would not be decisive. A survey of 12 vendors showed that nine vendors routinely guaranteed 90 percent removal, and five of these sometimes guaranteed 95 percent removal for short term “acceptance testing.” EPA also indicates that several of the successful FGD systems in Japan which the Electric Utilities claim are inapplicable and unavailable in the United States are provided to the Japanese by American vendors. Finally, the comments of the Industrial Gas Cleaning Institute (IGCI) which is a trade association representing the manufacturers of over 80 percent of American industrial air pollution equipment stated that:

The control equipment industry has the present capacity to design, manufacture, and install . . . FGD control systems which will meet the emission level requirements of the proposed [NSPS] [which required a 92 percent median], . . ,

Recognizing that the Clean Air Act is a technology-forcing statute, we believe EPA does have authority to hold the industry to a standard of improved design and operational advances, so long as there is substantial evidence that such improvements are feasible and will produce the improved performance necessary to meet the standard. We accept EPA’s documentation on the potential for improved performance of scrubbers to achieve a long term median of 92 percent. As a result, we uphold EPA’s judgment that the standard can be set at a level that is higher than has been actually demonstrated over the long term by currently operating lime scrubbers at plants burning high sulfur coal.

(b) The Reasonableness Of EPA’s Assumption About FGD Variability

Having determined that a median removal efficiency of 92 percent is achievable, the next question is whether EPA has properly accounted for performance variability. Variability or geometric standard deviation is a term used to describe the statistical distribution of levels of performance around the median. The relevance of variability in determining the achievability of a final standard can be seen from a simplified example. A system with 92 percent median efficiency and low variability might always achieve between 90 and 94 percent removal and thus always comply with the 90 percent standard. A system with a 92 percent median efficiency and high variability might achieve between 85 and 99 percent removal, and therefore it would not always comply with a 90 percent standard.

EPA based its variability assumption on its conclusion that the maximum variability of 0.36 percent at the Cane Run plant represents the outer boundaries of FGD variability. EPA explains that “variability in the performance of a well-operated FGD system will not exceed the maximum variability of the most variable well-run lime or limestone plant that has been tested [Cane Run].” EPA states that Cane Run represents a “worst case assumption” in five different respects:

it is based on lime/limestone FGD, which is more variable than regenerable and sodium-based FGD; it is based on'the most variable properly operated lime/limestone FGD tested; it is based on a peaking unit, which produces greater variability in flue gas volume than a base-load unit; it is based on maximum variability to be expected, rather than the average variability, at Cane Run; and it does not take account of techniques (automatic process controls and coal blending) that can reduce variability. The allowance for variability insures that the standard is achievable on a statistically consistent basis.

Initially we were skeptical about the validity of assuming that the variability sample of one plant was representative of the entire industry. Upon review we are satisfied that EPA’s case justifying its variability assumption is a reasonable one. The agency collected variability data from many plants including the seven plants in the agency’s data base for FGD median efficiency. The data from three of these plants was defined as “representative” for standard setting purposes. Of these three, Cane Run was the most variable; the rest were rejected for valid reasons, such as, the plants burned low sulfur coal, they used non-lime/limestone scrubbers, or they experienced scrubber malfunctions and thus were not representative of well operated lime FGD systems. For this reason we are not persuaded by the Electric Utilities’ argument that the aggregate data on variability, taken from all high sulfur burning plants in EPA’s data base, showed a higher variability (about 0.42-0.43) than Cane Run (0.36). In addition a consultant’s report on which EPA relied showed that variability could be reduced in future systems which incorporated specific design and operational improvements.

The Electric Utilities also argued that the variability experienced at the Cane Run plant is not representative of worst case variability because the variability is greater at the Bruce Mansfield plant, which is one of the other two plants EPA considers to be a well run lime/limestone FGD system. The Electric Utilities’ analysis of the Bruce Mansfield data concluded that FGD variability at such a plant could be at least as high as 0.38. Originally, EPA had not included in its variability analysis the Bruce Mansfield data relied on by the Electric Utilities. EPA argues that this additional data is unreliable for a number of reasons and should not be included in the variability data base. However, we are satisfied with EPA’s demonstration that even if the additional data are considered, they support a variability figure of 0.33 for the Bruce Mansfield plant. Therefore, the Bruce Mansfield data are consistent with the reasonableness of EPA’s conclusion of worst case FGD variability of 0.36.

In sum, the record supports the achievability of the level of FGD performance which is necessary to comply with the 90 percent standard by a long term median efficiency of 92 percent with a maximum variability of 0.36.

2. The Support for EPA’s Conclusion That the 90 Percent Standard Was Achievable by the Use of Coal Washing in Conjunction With Scrubbing

EPA has sufficiently established that a minimum 86 percent removal efficiency (on a thirty day rolling average)— derived from a 92 percent median with 0.36 variability — is achievable on a continuous basis by the use of scrubbers alone. We now consider whether coal preparation techniques can enable utilities to increase the overall removal efficiency to meet the 90 percent standard. EPA claims that when physical coal cleaning or coal washing (the most prevalent method of coal preparation) is used together with “pulverization” and/or “ash retention techniques,” then FGD systems capable of only 85 percent removal can meet the 90 percent standard. The Electric Utilities argue, not without cause, that the record underlying EPA’s conclusions about the supplemental sulfur removal potential of pulverization and ash retention is deficient. They also claim that EPA has no basis for expecting that the removal efficiencies achieved by these individual technologies can be added together when the technologies are combined, since some of the sulfur each system is designed to remove may have been eliminated already through the prior use of another sulfur reduction technology. However, we do not find it necessary to reach the merits of EPA’s case for an additional 10 percent reduction based on pulverization and ash retention because we are satisfied on the record that coal washing used in conjunction with FGD will achieve the standard.

(a) Description of the Coal Washing Process

Coal washing is a widely practiced and relatively inexpensive method of removing sulfur from coal currently used on approximately one-half of the coal produced in the United States including about 40 percent of the coal destined for electric utility plants. Sulfur reduction under current commercial coal washing practices varies with several factors.

Coal washing separates unwanted sulfur from coal by suspending crushed coal in a fluid, then separating the dense sulfur particles, which sink to the bottom, from the less dense particles of cleaned coal, which rise to the top. Commercially available coal washing processes remove inorganic sulfur, e. g., high density pyrite crystals, but not organic sulfur which is chemically bonded to the coal. Three factors determine the maximum percentage reduction of sulfur: (1) the relative proportions of organic (non-washable) and inorganic pyritic (washable) sulfur, (2) the particle size to which the raw coal is crushed before it is suspended in the separating fluid, and (3) the specific gravity of the fluid in which the coal is immersed.

The proportions of organic and pyritic sulfur vary widely depending on the coal. While coal washing can remove from 35 to 70 percent of pyritic sulfur, the total percentage of removable sulfur is limited by the amount of nonwashable organic sulfur in the coal, which ranges from 30 to 70 percent of total sulfur content. High sulfur coal has a high proportion of pyritic sulfur compared to low sulfur coal. For this reason, it is easier to wash a given percentage of sulfur out of high sulfur coal than low sulfur coal.

As a general rule, when coal is crushed into smaller particles, more sulfur can be washed out. However, the smaller the coal particles, the more coal that is inadvertently washed out with the sulfur, and the more energy that is consumed in processing the coal. Both of these kinds of energy losses are measured in terms of the percentage of Btu’s in raw coal that are recovered after washing. For example, standard coal washing results in an energy loss of from 5 to 20 percent, which translates to a Btu recovery ranging from 95 to 80 percent. In addition to energy loss, handling and processing costs increase with the amount of crushing. These economic constraints limit the maximum amount of coal washing that is feasible in any given situation.

The specific gravity at which the separation is performed is also a critical factor. The lower the specific gravity the greater the amount of pyritic sulfur that is eliminated. However, as lower specific gravities are used more coal is also lost and thus fewer Btu’s are recovered.

Lowering the sulfur content of coal by a given percentage through coal washing reduces the potential sulfur dioxide emitted from burning the coal by the same percentage since the sulfur in coal is converted into sulfur dioxide in a fixed proportion. The percentage of sulfur reduction achieved by a coal washing in turn reduces the level of efficiency of a scrubber required to achieve the overall 90 percent reduction standard. But there is significantly less than a percent for percent trade-off between coal washing and necessary scrubbing. Every percent removed by coal washing reduces the needed efficiency of FGD by much less than one percent. A brief example will illustrate the point: given a coal with uncontrolled emissions of 10 Ibs./MBtu, the final standard would require a 90 percent overall reduction to 1.0 Ibs./MBtu. If coal washing reduced potential emissions 25 percent to 7.5 Ibs./MBtu, then the scrubbers would have to eliminate 6.5 Ibs./MBtu to limit emissions to 1 lb./MBtu. This means that the scrubbers must operate at 87 percent reduction efficiency.

(b) The Percentage Reduction Achievable By Washing High Sulfur Coal

EPA asserts that it is conservative to assume that a 27 percent reduction in sulfur content is achievable through washing high sulfur coals (greater than 6.0 lbs./MBtu). If the agency is correct, then a 90 percent total reduction can be achieved even in the “worst case” scenario involving high sulfur coals with a scrubber operating at 86-87 percent efficiency. Coals with sulfur content less than 6.0 lbs./MBtu are not subject to the 90 percent standard, thus a 27 percent reduction by coal washing is unnecessary on those coals. The Electric Utilities do not agree that 27 percent removal has been demonstrated for washing these high sulfur coals, or that the 90 percent standard can be achieved on them by a combination of coal washing and scrubbing.

Our inspection of the record reveals a wealth of technical data on the washability of every type and variety of coal in the United States. A Bureau of Mines (“BOM”) Report, prepared in 1976 and included in the record of this rulemaking, examined the percentage of sulfur removal by different levels of washing in 455 raw coal channel samples in different regions, states, and coal beds. This study concluded that the national average washability was 27 percent with crushing to IV2 inch top size, specific gravity at 1.6 and the average sulfur content of all the coal sampled at 4.9 lbs./MBtu. The main regions producing high sulfur coal — Eastern Midwest and Northern Appalachia — averaged washability of 30 percent and the Western Midwest averaged just under 30 percent with crushing to IV2 inch top size and specific gravity at 1.6. The washability of specific coal could exceed the average if its sulfur content exceeded the average, if there was greater size reduction, or a higher specific gravity was employed. EPA concluded initially from the BOM data that a 35 percent potential sulfur reduction was reasonable for coals of 2.5 lbs./MBtu or more, but later assumed this level of reduction was applicable for coals of 5 lbs./MBtu or more, including, of course, the 6 lbs./MBtu sulfur coals for which washing is essential to meet the standard.

In the final rule, however, EPA appeared to back off from the 35 percent figure to the more conservative 27 percent which was, in effect, endorsed by the NCA and the Electric Utilities, who had objected that the 35 percent figure was “optimistic by 5 to 10 percentage points.”

In the denial of the Electric Utilities’ petition for reconsideration EPA cited NCA’s data and said:

On high-sulfur midwestern coals that would be subject to the 90 percent reduction requirement an average of 27 percent sulfur removal was achieved by conventional coal washing plants in 1978.. . . These data represent current industry practice and do not necessarily represent full application of state-of-the-art in coal cleaning technology.

The Electric Utilities’ own consultant wrote that “[t]he available docket information basically supports the 27 percent average coal washing credit cited by EPA.”

There is little doubt that the record supports an average 27 percent coal washing reduction potential on high sulfur coal. The remaining question is whether such an “average” figure can be relied upon to support the requirement of section 111 that the “achievability” of a standard must be “demonstrated.” The Electric Utilities argue that the 27 percent does not take account of variability so that washing on the low ends of the “average” would not be sufficient to meet the standard. Both NCA’s limited data and the Bureau of Mines’ seam by seam data indicate deviations from the “average” sulfur removal attainable by washing the coal sampled. The data, however, also suggest to us that fluctuations in the removal potential of washing are closely tied to the varying characteristics of the coal itself (primarily its sulfur content) and not the reliability of the washing process. Thus, instances where coal washing might achieve below 27 percent would seem to involve treatment of coal whose sulfur content is considerably less than 6.0 lbs./MBtu and therefore not subject to the 90 percent reduction standard.

In any event, the best answer to the variability argument seems to lie in the mechanics of the compliance provisions of the rule that set out the methods of taking coal washing credits. A standard may be based on reliable data about the “average” removal from coal washing if the utilities who must comply with the standard are permitted the same leeway in “averaging” for compliance purposes. We believe that is so in this case for the following reasons. In order to take credit for coal washing the sulfur content of the raw coal and its sulfur content after washing must be determined in advance of feeding the coal into the boiler. Under EPA’s regulations coal supplies can give utilities a certificate of credits with each lot of washed coal fuel delivered [or for all lots delivered for a calendar quarter]. The certificates have to show (1) sulfur analysis of a coal input and output for the washing plant, (2) the quantity delivered, (3) the heat content, and (4) the calculation of pretreatment credit. After the utility plant receives the fuel and the pretreatment certificate, a summary of credits for all fuel received in a calendar quarter is prepared and averaged to obtain a quarterly pretreatment credit. This average credit is applied to 30 day periods in the following quarter. That is, for a utility to determine its present compliance level it combines the “average” coal washing credit from the previous quarter with the FGD control level in each 30 day measuring period in the current quarter. If an average of 27 percent removal by coal washing is achieved on a quarterly basis then the utility is credited with 27 percent toward compliance in the next quarter whether or not washing of certain lots varied above or below the 27 percent level. This allows a utility to monitor its coal supply and affords flexibility in meeting the standard. If incoming coal supplies threaten to increase the quarterly average to unacceptable levels, then buying for the rest of the quarter can be adjusted. EPA expected that utilities would enter into contract arrangements with their suppliers to obtain and guarantee that coal supplies meet the needed treatment criteria.

If for some reason a utility obtains coal that has not been washed to the desired level the result is not an automatic violation of the standard, as the Electric Utilities imply. Rather, utilities have the option of: (1) not burning the coal, (2) enforcing their supply contracts, or (3) burning the coal realizing that when averaged with other quarterly supplies the credit needed to comply will be obtained.

Thus the variability of individual lots of washed coal does not assume so critical a role as variability does in FGD systems which are under continuous monitoring. Since there is no doubt that a 27 percent “average” is achievable with the highest sulfur coals that must meet the 90 percent reduction, we believe that the standard can be upheld on the basis of the coal washing data in the record.

The Electric Utilities’ final argument is that the record contains no data on the actual combined use of coal washing and FGD, and that EPA has not demonstrated that the standard is achievable simply by hypothesizing that coal washing and FGD can work together.

We do not believe that, on the facts in this record, such an actual demonstration was necessary. The record is replete with documentation that lower sulfur coal is easier to scrub than higher sulfur coal, and the Electric Utilities have not cited nor have we found any evidence that washed coals create any special problems for scrubbers. The main difference between washed and unwashed coal of the same sulfur content is that the washed coal contains fewer impurities that may be expected to interfere with FGD performance. In fact, the record contains reports analyzing the potential reductions achievable by the combined technologies and evidence that washing can be expected to increase FGD performance. At an empirical level, since 40 percent of the coal now being used by utilities has been washed, the industry has certainly had the requisite experience to anticipate and document any potential problems.

For all of the foregoing reasons we find that EPA has adequately demonstrated the achievability of the 90 percent standard.

IV. THE STANDARD FOR EMISSION OF PARTICULATE MATTER

Most particulates emitted from electric utility sources come from coal-fired units. In 1976, for example, particulate emissions from coal-fired electric utilities accounted for 3.42 million out of 3.57 million tons coming from all electric utilities and 14.9 million tons from sources of all kinds. The former NSPS limited emissions of particulate matter to 0.10 lbs./MBtu. The revised standard limits emissions to 0.03 lbs./MBtu, and is based on the performance of either a well designed, operated and maintained electrostatic precipitator (“ESP”) or a baghouse control system. The Electric Utilities, the only party to challenge the particulate standard, argue that the record does not support the conclusion that the promulgated standard is achievable by either ESP or baghouse technology.

A. Technical Background

1. ESP Control Technology

Since ESP’s were introduced to the utility industry in the 1920’s, they have become the most widely used means of controlling particulate emissions from coal-fired boilers. An ESP removes particles from a gas exhaust stream by electrically charging the particles and then attracting the charged particles to metal plates having the opposite charge. The size of the collecting plates and thus the size of the ESP are directly related to the capability of the ESP to control emissions. The larger the surface area of the ESP collecting plates the greater the ability of the ESP to remove particles from flue gas, assuming all other factors that affect ESP performance are held constant. Not surprisingly, installation and operating costs also increase with the area of the collecting plates. On the other hand, the volume of particulate-laden gas that needs to be treated by an ESP affects ESP effectiveness inversely. As the gas volume increases, the effectiveness of a given ESP decreases, again assuming all other factors are held constant. The ratio of the size of the collecting plates to the volume of gas treated, is known as the specific collecting area (“SCA”). SCA is measured in terms of square feet of plates per 1000 actual cubic feet per minute of gas (“Ft2/1000ACFM”). The greater the SCA the more effective the ESP. Increasing the area of the collecting plates increases the SCA and ESP effectiveness; in contrast, increasing gas volume decreases the SCA and ESP effectiveness.

Two other important determinants of ESP effectiveness and cost are the characteristics of the fly ash produced by the burned coal and the temperature of the gas exhaust stream. The ash produced by the combustion of some low sulfur coals is highly resistant to electrical charging, which creates a problem for ESP collection. Generally, a larger SCA is needed for highly resistant ash than would be needed for cleaning the ash of most coals “whose resistivity is below the level where problems occur.” For these high resistance coals, ash resistivity is at a maximum in the temperature range experienced after the flue gas exhausts from the air combustion preheater (downstream or “cold side” of the preheater). Conversely, the ash resistivity is much lower at the “hot side” (upstream) of the preheater. Consequently, high resistivity coal ash is easier to collect on the hot side than on the cold side of the preheater. However, this does not always mean that a smaller ESP can be applied on the hot side than on the cold side because gas volume is greater on the hot side. The advantages of hot side ESP are offset also by greater construction costs due to higher quality of materials, thicker insulation, and special design features to accommodate the expansion and warping potential of the collection plates. A typical ESP is shown as Figure 19 in the appendix to this opinion.

2. Baghouse Control Technology

Baghouse control of particulate emissions is an increasingly popular alternative to ESP’s among electric utilities, largely because baghouses are not affected by particulate resistivity to electrical charge, and thus are less expensive to operate for power plants burning low sulfur coals with high resistance ash.

In a baghouse system, particulate-laden gas is passed through a fabric filter so that particulates in the gas are retained on the upstream or dirty-gas side of the fabric. In a baghouse system the dirty gases flow into the housing, upward through the bags, and then out of the clean gas outlet. Typical baghouse systems are shown in Figures 20 and 21 in the appendix to this opinion.

A baghouse consists of numerous tubular fabric bags (each about one foot in diameter and thirty feet long) arranged in compartments or cells parallel to each other, standing like a stack of porous straws in a box. The flue gas from the boiler is divided so that a small fraction of the gas passes through the individual bags. Large bag-house systems can be designed as one large cell or module or many individual modules. With several modules, one module can be taken out of service for maintenance without affecting the operation of the other modules. If enough modules or isolated components are provided, even the largest pulverized coal-fired steam generators can be kept on line at full load while necessary maintenance is performed.

Two determinants of baghouse performance are the “air-to-cloth” ratio and the “pressure drop.” For a given flue gas stream, a greater fabric surface (larger baghouse) yields a lower air-to-cloth ratio. The pressure drop represents the pressure (measured in inches of water (“In.H20”)) required to force the flue gas through the fabric bags. For a given quantity of flue gas, the pressure drop increases as the fabric area decreases, since greater force is needed to push the flue gas through a smaller filter surface. Accordingly, at any boiler operating at full load, a larger air-to-cloth ratio (smaller baghouse) tends to be associated with a higher pressure drop, while a lower air-to-cloth ratio (larger bag-house) tends to be associated with a lower pressure drop.

There is a maximum pressure drop that can be achieved by a given boiler operating at full capacity. If the baghouse is undersized, that is, if the air-to-cloth ratio is too high, then the boiler will not be able to achieve full load. Thus, unlike ESP systems, where undersizing does not affect the capacity of the steam generator, but does affect the efficiency of the emission control system, the penalty for undersizing a bag-house is loss of boiler capacity.

B. The Evolution of the Particulate Standard

In 1975, EPA began to investigate whether the 0.10 lbs./MBtu standard for particulates should be revised because the existing techniques for control of particulate emission appeared to be more effective than when the standard was originally promulgated in 1971. By 1976, EPA’s research determined that there were, in fact, ESP systems installed at coal-fired power plants which were controlling emissions substantially below the 1971 standard. At this point EPA sought to acquire additional data on the achievability of a stricter standard. EPA attempted to locate plants which generated high resistivity ash and were equipped with ESP’s with large SCA’s. With the assistance of the Industrial Environmental Research Institute (“IERL”) and the Industrial Gas Cleaning Institute (“IGCI”), EPA located six sources meeting these criteria. All of these sources were surveyed by plant visits: EPA found that “adequate emission test data were available” for three of the sources, two of the other three sources were tested by EPA, and the sixth source was tested by the utility company with an EPA observer present. Additional emission test data were gathered from IERL and State agencies to form a data base from tests of twenty-one different ESP systems. On the basis of this data base EPA concluded that ESP’s are capable of achieving a limit of 0.03 lbs./MBtu even when the most difficult to control fly ash is generated. In the preamble to the final rule, EPA stated its judgment that utilities firing low sulfur coal (less than 1.0 percent) must have an ESP with a hot side SCA of 650 Ft2 /1000ACFM or a cold side SCA of lOOOFt2 /1000ACFM to achieve the standard. EPA suggested that firing medium sulfur coals (between 1.0 and 1.9 percent) would require a hot side SCA in excess of 452 Ft2 /1000ACFM or a cold side SCA in excess of 435 Ft2/1000ACFM, while firing high sulfur coal would require a cold side SCA of at least 360 Ft2/1000ACFM. No hot side SCA figure was recommended for utilities firing high sulfur coal. EPA concluded that all of these SCA’s were reasonable considering cost, energy, and nonair environmental impacts.

In January 1977, while EPA was reassessing the capability of ESP control, the agency found that baghouse technology was developing well enough to warrant considering baghouses as an alternative to ESP’s for even the largest utilities. EPA made a survey of sixteen baghouse installations and from this survey EPA concluded that the actual effectiveness of baghouses could prove equal, if not superior to ESP systems. Although the baghouses surveyed were installed at small plants, the agency found that the systems were composed of numerous individual cells and that even the largest steam generator could use baghouse control by increasing the number of cells as needed to handle the gas flow. Two plants were visited and subsequently tested by EPA in the spring and summer of 1977. This data base was supplemented by test results provided by IERL and by test data from the State of West Virginia to form a data base of tests from eight different bag-house systems. On the basis of this data base EPA concluded that baghouses with an air-to-cloth ratio of 2ACFM/Ft2 will achieve the standard at a pressure drop of less than 5 In.H20. These specifications were considered reasonable in light of cost, energy, and nonair environmental factors.

Although finding that either technology could be employed at a reasonable cost to achieve the standard, EPA predicted that utilities would rely on ESP’s for high sulfur coal applications and baghouses for low sulfur coal applications because of cost advantages.

C. The Achievability of the Standard

In order for EPA to demonstrate the achievability of the standard for particulate matter it must: (1) identify variable conditions that might contribute to the amount of expected emissions, and (2) establish that the test data relied on by the agency are representative of potential industry-wide performance, given the range of variables that affect the achievability of the standard. National Lime Association v. EPA.

Citing these principles, the Electric Utilities argue that EPA’s data base does not show that the particulate matter standard is achievable on a continuous basis, for either ESP or baghouse control. Initially, the Electric Utilities fault EPA’s analysis of ESP and baghouse performance because it did not take into account whether the standard is achievable by utilities firing lignite coal, which they contend is a relevant variable. EPA counters that it did consider the achievability of the standard with lignite, and that it concluded that lignite was not a relevant factor because it was no more difficult to control lignite emissions than the emissions from other high resistivity coals. Most of the Electric Utilities’ other objections are to the representativeness of the test data for both ESP’s and baghouses. They say that the ESP and baghouse test results are incomplete, that the samples are too small and that the data reflect only short term performance while the standard requires long run continuous compliance. In addition, they claim that EPA has failed to reveal its methods of data collection and the conditions present during the tests. Finally, the Electric Utilities contend that the baghouse data are not representative because all of the data available at the time of promulgation of the standard were from small scale baghouse operations whereas the data obtained after promulgation from commercial size installations actually refute EPA’s conclusions. These contentions require that we evaluate EPA’s data in greater detail. As discussed below we uphold the particulate standard despite concern about EPA’s ESP data because we find that the agency’s baghouse data alone establish the achievability of the standard.

1. EPA’s ESP Data

EPA satisfied its burden under the first prong of the National Lime test by describing the variable conditions that could be expected to affect ESP performance (e. g., coal ash characteristics, ESP size, gas volume and flow, maintenance practices, etc.). However, EPA has not met its burden for establishing that its ESP data are representative of industry-wide performance under the second prong of the National Lime test for achievability. We reach this conclusion even if EPA is correct that it devoted enough attention to another potential variable — the impact of firing lignite coals on the achievability of the standard.

EPA collected emission data from twenty-one ESP-equipped steam generating units firing relatively low sulfur coal (0.4 to 1.9 percent). EPA explained that it “evaluated emission levels from units burning relatively low-sulfur coal because it is more difficult for an ESP to collect particulate matter emissions generated by the combustion of low-sulfur coal than high-sulfur coal.” But the agency’s own background document identifying the relevant performance factors does not list the sulfur content of coal as one of the variables and instead focuses on the resistivity of coal ash. While some low sulfur coals produce high resistivity ash, “sulfur content of the fuel alone is an extremely poor predictor of the resistivity for low sulfur fuels.” Although EPA identified resistivity as an important variable, its reported data do not indicate the resistivity of the coal fired at the test units. In contrast, two nonagency reports on the record concerning ESP performance include resistivity data.

The ESP test results are listed in a table in the Background Information Document for the Proposed Standard which is shown as Figure 22 in the appendix to this opinion. EPA reported that nine of the twenty-one units tested performed better than the 0.03 lbs./MBtu standard even though none of the twenty-one ESP units were designed to achieve this level of performance. Of the twelve units that exceeded the 0.03 lbs./MBtu level none experienced emissions greater than 0.05 lbs./MBtu. The former standard had been 0.10 lbs./MBtu or twice the worst test performance. Superficially, these performances appear to support the conclusion that ESP’s can be designed to achieve the 0.03 lbs./MBtu standard. However, we have serious reservations about the completeness of the reported data for the twenty-one ESP-equipped units.

The table in which EPA’s ESP data is compiled lists complete data for only twelve of the twenty-one units. Of this group only two of the units with complete data were reported as achieving the standard and only one of these two was firing low sulfur coal (less than 1.0 percent). The data that is missing on the table includes the SCA measurement and whether the ESP is hot side or cold side. EPA’s background documents identify these two factors as critical.

In another table, shown as Figure 23 in the appendix to this opinion, EPA lists a summary of data on “difficult” ESP cases. This table reports data for seven ESP units firing coal less than 1.0 percent. The data of six of these units are repeated from the table of twenty-one units, but there were more than six units — eleven to be exact — in the previous table that fired less than 1.0 percent sulfur coal. EPA offers no explanation for this selectivity other than the statement that the seven difficult cases were selected based on the “reports of owners and ESP vendors that the low sulfur coals fired at the plant produced a difficult to collect ash.” This statement calls attention to the fact that something more than just the sulfur content of the coal is relevant to the difficulty of ESP collection, and EPA has not shown that its data account for this factor — the resistivity of the ash. The seventh unit (unit 22) listed on the table of difficult cases was not included on the first table of units and it represents an additional unit that EPA does not appear to discuss or explain anywhere else on the record. While complete data for all seven of the so-called difficult cases are listed, only one of these cases limited particulate emissions below the 0.03 level. This one unit then is EPA’s substantiation that the standard is achievable “even in the most difficult eases.”

We note that EPA’s data are inadequate in other respects. First, the background document which contains the data reveals very little information about the duration of the tests and the conditions under which they were taken. We have been able to find some partial references in the joint appendix which disclose some of this information. We also are aware that the background document includes a citation to a test report for each unit tested. These reports are not included in the joint appendix, and no reference to the administrative docket is offered in most of EPA’s citations. Presumably, some of the information that would be useful to our review is included in these documents. However, especially in a case of this magnitude and complexity, it is not reasonable for the agency to expect the court on its own to gather together all of the scattered pieces of information that are necessary to make a coherent whole.

The Electric Utilities have also argued that the record does not reveal EPA’s method of data collection. We believe, however, that throughout the rulemaking process EPA has given notice of the established test methods relied on; thus, the data base is not objectionable on this basis.

Our concerns with the lack of documentation for EPA’s data base are somewhat allayed by independent evidence on the record which tends to support the reasonableness of the agency’s conclusions about ESP performance. High efficiency particulate removal has been practiced for decades on high and medium sulfur coal. Although EPA did not believe that utilities would use ESP’s in high resistivity low sulfur coal applications, it found that ESP control of these cases was feasible so long as the ESP’s were large enough — with a hot side SCA greater than 650 FtVlOOO ACFM or a cold side SCA as large as 1000 FtVlOOO ACFM. These figures are corroborated by an independent report prepared in 1974. Another report, prepared in 1978 by the Electric Power Research Institute (“EPRI”) suggests that high efficiency removal by ESP’s is feasible but questions whether it would be economical to drop much below the former NSPS of 0.10 lbs./MBtu. The EPRI report concluded that baghouses would become the economical choice for all coals with standards below the 0.10 lbs./MBtu level. Despite the presence of some evidence in the record that suggests that EPA’s findings are reasonable, the agency’s presentation of its own data on which it says it is relying does not provide the guarantee required by National Lime that the test results be representative of industry-wide performance.

2. EPA’s Baghouse Data

We can uphold the 0.03 lbs./MBtu standard for particulates because we are satisfied that there is substantial evidence on the record supporting the achievability of the standard by baghouse technology. The preamble to the final rule refers to this evidence, which includes extensive tests of small scale installations, limited data from one full scale commercial sized operation, in addition to industry practices that indicate that baghouse control technology is a viable method of complying with the standard. Evidence added to the record since promulgation and evaluated with the petitions for reconsideration confirms the reasonableness of EPA’s conclusion that the standard is achievable with baghouses.

EPA identified, in accordance with National Lime, the variable conditions that affect baghouse performance (e. g., bag-house size, pressure drop, cleaning, maintenance, etc.). In accordance with the second prong of the National Lime test the agency accounted for these variables with the following data: EPA’s data base from small scale baghouse operations was comprised of fifty emission test runs conducted at eight baghouse-equipped generating units. Although none of these baghouse units was designed to achieve the 0.03 lbs./MBtu level (again EPA does not report what level the baghouses were designed for), forty-eight of the test results achieved this level of emissions and only one test run at each of two units exceeded the 0.03 lbs./MBtu level. Neither of these two tests appears to have exceeded the 0.05 lbs./MBtu level. The data are summarized in a table found in the Background Information Document for the Proposed Standard and are shown as Figure 24 in the appendix to this opinion. Although complete data are not provided for all of the tested units, the omissions are not as critical as was the case with the agency’s unsatisfactory ESP data and do not frustrate our ability to determine that the data supports the agency’s stated rationale.

Complete data are listed for all four of the units tested by EPA methods. At the other four units, West Virginia test methods were used which EPA states are similar to its own test methods. In these cases data are not given for air-to-cloth ratios and pressure drops. However, all of the performances at the four EPA tested units, for which complete data are listed, except for one test run at Unit 8, achieved the 0.03 Ibs./MBtu standard. At these installations, three of the four units that never exceeded the standard reported pressure drops less than or equal to 5 In. H20 (ranging from 2.1 to 5.0 In. H20). The fourth unit (Unit 8) that failed to achieve the standard on one test listed pressure drops ranging from 8 to 10 In. H20. Air-to-cloth ratios for all four of the EPA tested units ranged from 1.9 to 3.0 ACFM/Ft2. From this data it is possible to discern how EPA derived the baghouse specifications it judged were necessary to achieve the standard. We see that its judgment that an air-to-cloth ratio of 2 ACFM/Ft2 will achieve the standard at a pressure drop less than 5 in. H20 was, if anything, conservative.

All of the small scale units were less than 44 MW. Before announcing the final standard EPA was able to obtain test data from one new unit with 350 MW capacity. The baghouse control system for this facility was designed to achieve 0.01 lbs./MBtu, or three times less emissions than allowed by the standard. The baghouse system there had a pressure drop of 5 in. H20 and an air-to-cloth ratio of 3.32 ACFM/Ft2 which is undersize according to EPA’s estimate that a 2.0 ACFM/Ft2 air-to-cloth ratio would be appropriate for a pressure drop of 5 in. H20. In the preamble to the final rule EPA reported:

Although some operating problems have been encountered, the unit is being operated within its design emission limit and the level of the standard. During the testing the power plant operated in excess of 300 MW electrical output. Work is continuing on the control system to improve its performance.

In addition to the operating experience from eight small scale facilities and one large scale facility, EPA noted that the trend in the utility industry reflected considerable confidence in full scale baghouse technology:

As of May 1979, at least 26 baghouseequipped coal fired utility steam generators were operating, and an additional 28 utility units are planned to start operation by the end of 1982. About two-thirds of the 30 planned baghouse-controlled power generation systems will have an electrical output capacity greater than 150 MW. . . ,

The Electric Utilities vigorously argue that EPA’s data are not representative of the performance at full scale electric power plants and say that there are technological barriers to scaling baghouses up to commercial size facilities. These concerns are belied by the large numbers of utilities that are, in fact, moving to baghouse control systems. In any event, EPA has acknowledged since the standard was proposed that its performance data are based on small scale plants (which were the only size bag-house installation available at the time). We cannot fault EPA for failing to produce nonexisting data on baghouses at larger plants. We only can look carefully at the smaller plant data, as we have done, and at EPA’s explanation for the representativeness of these data. EPA reasons that data obtained from small units were representative of the performance of large units because baghouses are designed and constructed as modules, and therefore a large unit basically involves more modules. This explanation is reasonable and borne out by the record. For example, the largest baghouse system in operation at the time of promulgation — a full size 350 MW power plant — had twenty-eight baghouse modules, each servicing 12.5 MW of generating capacity. While this new unit experienced some operation difficulties such as bag failure and high pressure drops, EPA explained that the failures were temporary and due to undersizing the baghouse by 40 percent from the recommended air-to-cloth ratio as well as to problems associated with working out bugs in a new system. EPA found that these problems were surmountable technological barriers to operating bag-houses on a large scale. At another plant, four pulverized coal-fired boilers supplying a total of 112.5 MW have been retrofitted with baghouses. As the Electric Utilities state, this utility station employs four small baghouses serving less than 30 MW each. All of the baghouses in this commercial size station have consistently complied with the standard. At still another utility plant two units have been retrofitted with baghouses and are guaranteed by the manufacturer to achieve 0.03 lbs./MBtu, but test results on these plants are not available. This record demonstrates that EPA’s test data are representative of full scale performance.

The Electric Utilities also object that the agency’s baghouse data are unrepresentative because only two of the eight small scale units were utility boilers while the remaining six units were industrial boilers and most stoker-fired as opposed to pulverized coal-fired. But again EPA has offered a rational explanation for the representativeness of these data: “[ejffective baghouses are designed on a multicell basis. The prime difference between an industrial and a utility baghouse is the number of cells. Consequently, data on the effectiveness and reliability of industrial boiler bag-house design is applicable to utility steam generators.” The reasonableness of the explanation is verified by the large number of utilities adopting baghouses as control technology.

The Electric Utilities also rely on post-promulgation data acquired from two full size plants to refute EPA’s conclusion that the 0.03 standard is achievable by baghouse control at reasonable cost. In their petition for reconsideration and on this appeal the Electric Utilities argue that the costs of operating baghouses at Southwestern Public Service’s Harrington Station (“Harrington”) and Texas Utility Generating Company’s Monticello Station (“Monticello”) are in excess of EPA’s estimated costs for bag-house control. They contend that the bag replacement costs during the first year of operation, approximately $250,000 at the 350 MW Harrington unit and $321,000 for each of the two 305 MW Monticello units, surpassed EPA’s estimates. To derive EPA’s estimated figures for baghouse replacement it is necessary to refer to several different documents containing economic data which are scattered throughout the joint appendix. Then, because EPA’s estimates are only listed for units of 200, 500, and 1000 MW, it is necessary to interpolate between the 200 and 500 MW cases to obtain the correct estimate for the Harrington 350 MW unit and Monticello 305 MW units. These calculations show that the estimated cost of bag replacement for a unit the size of Harrington is $440,000 and $390,000 for Monticello size units. These estimated allowances exceed the actual bag replacement costs for the two stations in question. Thus, we find that EPA was correct in stating in its denial of the petition for reconsideration that “cost estimates developed by EPA provide liberal allowance for start-up and continued maintenance.”

The Electric Utilities also maintained that the high pressure drop encountered at Harrington and Monticello would increase operating costs. EPA responds first that the Harrington plant is undersize, and that both plants experienced difficulties due to poor bag design and fabric selection. Because of these temporary problems, costs at Harrington and Monticello are not indicative of the costs at a properly operated baghouse installation. Furthermore, EPA found that even if the high pressure drops predicted by the Electric Utilities were maintained (11 In. H20 as compared with EPA’s recommended 5 In. H20) the result would be a cost increase of $191,000 per year. Since this increase amounted to a 4.5 percent increase in the total annualized cost projected for full size baghouse operation and less than 1 percent increase relative to utility operating costs, EPA concluded that the Electric Utilities’ forecasted cost was not excessive and did not make the cost of compliance with the standard unreasonable. This is a judgment call with which we are not inclined to quarrel. Besides, EPA reported that the 11 In. H20 pressure drop predicted by the Electric Utilities had been reduced by corrective measures at Harrington to 8 In. H20. This level of pressure drop would reduce the annual cost increment by about $90,000 from $191,000 at 11 In. H20.

In sum, EPA has sufficiently established that the standard for particulate emission is achievable by baghouse control by accounting for relevant variables and by demonstrating the representativeness of its data. The post-promulgation record does not require a contrary conclusion or indicate that the standard is unreasonably costly. For these reasons we affirm the particulate standard on the basis of the performance of baghouse technology.

V. THE 1.2 LBS./MBTU EMISSION CEILING

EPA proposed and ultimately adopted a 1.2 lbs./MBtu ceiling for total sulfur dioxide emissions which is applicable regardless of the percentage of sulfur dioxide reduction attained. The 1.2 lbs./MBtu standard is identical to the emission ceiling required by the former standard. The achievability of the standard is undisputed.

EDF challenges this part of the final NSPS on procedural grounds, contending that although there may be evidence supporting the 1.2 lbs./MBtu standard, EPA should have and would have adopted a stricter standard if it had not engaged in post-comment period irregularities and succumbed to political pressures. EDF raises its procedural objections in the context of its view that a more stringent emission ceiling would have been better than the 1.2 lbs./MBtu limit because it would decrease total emissions significantly without impeding the production or use of coal. Although the substantive validity of the 1.2 lbs./MBtu standard is not before the court, it is not possible to evaluate EDF’s procedural argument without first examining the evolution of the standard and EPA’s explanation for adopting the emission ceiling.

A. EPA's Rationale for the Emission Ceiling

EPA explained in the preamble to the proposed rule that two primary factors were considered in selecting the 1.2 lbs./MBtu ceiling: FGD performance, and the impact of the ceiling on high sulfur coal reserves. EPA further explained that it had considered whether to propose a 1.2 lbs./MBtu limitation with and without three exemptions per month. EPA’s modeling analysis showed that under either option there would be no significant differences in total national production and there would be sufficient reserves available to satisfy national demand for coal. However, EPA predicted that on a regional basis a 1.2 lbs./MBtu ceiling without exemptions would adversely affect the Midwest. Consequently, EPA proposed that the emission limitation should have three exemptions but solicited comments on the level of ' the emission limit and the appropriateness of the 3 day exemption.

Following the September 1978 proposal the joint interagency working group investigated options lower than the 1.2 lbs./MBtu ceiling, according to EPA, in order “to take full advantage of the cost effectiveness benefits of a joint coal washing/scrubbing strategy on high-sulfur coal.” The joint working group reasoned that since coal washing is relatively inexpensive, an emission ceiling which would require 90 percent scrubbing in addition to coal washing “could substantially reduce emissions in the East and Midwest at a relatively low cost.” Since coal washing is a widespread practice, it was thought that the 1.2 lbs./MBtu proposal would not have a seriously detrimental impact upon Eastern coal production. During phase two EPA analyzed 10 different full control and partial control options with its econometric model. These various options included emission ceilings at the 1.2 lbs./MBtu, 0.80 lbs./MBtu and the 0.55 lbs./MBtu levels. The modeling results, published before the close of the public comment period in December 1978, confirmed the joint working group’s conclusion that the 1.2 lbs./MBtu standard should be lowered. The results of the phase two modeling exercise were cited by internal EPA memoranda in January and March 1979 as a basis for lowering the 1.2 lbs./MBtu standard. After the phase two modeling, however, EPA undertook “a more detailed analysis of regional coal production impacts,” using BOM seam by seam data on the sulfur content of the reserves and the coal washing potential for those reserves. This analysis identified the amount of reserves that would require more than 90 percent scrubbing of washed coal to meet alternative ceilings.

As a result of concerns expressed on the record by NCA and others about the impacts of more rigorous emission ceilings, EPA called a meeting of principal participants in the rulemaking for April 5, 1979. At the meeting EPA presented its new analysis which showed that a 0.55 lbs./MBtu limit would require more than 90 percent scrubbing on 5 to 10 percent of Northern Appalachian reserves and 12 to 25 percent of Eastern Midwest reserves. A 0.80 ceiling would require more than 90 percent scrubbing on less than 5 percent of the reserves in each of these regions. NCA presented its own analysis on the sulfur content and washability of reserves held by its member companies, “a very small portion of the total reserves but including reserves which are planned to be developed in the near future.” The NCA data confirmed the EPA analysis within 5 percentage points. At the same meeting the Administrator “reviewed his assessment of state of the art coal cleaning technology” and accepted NCA’s recommendation that common practice, i. e., crushing to IV2 inch top size rather than to smaller sizes with separation at 1.6 specific gravity, be used as the standard when evaluating the impact of coal washing.

After the April 5 meeting EPA also “concluded that the actual buying practices of utilities rather than the mere technical usability of coals should be considered.” This exercise was expected to identify high sulfur coals that utilities would not use in order to avoid the risk of failing to satisfy the standard. EPA assumed that utilities would only purchase coal that would provide about a 10 percent margin below the emission limit in order to minimize risk, and, further that utilities would only purchase coal that would meet the emission limit (with the 10 percent margin) with no more than a 90 percent overall reduction in potential emissions. EPA claimed that these assumptions reflected utility preference for buying washed coal for which only 85 percent scrubbing is needed to meet both the percent reduction and the emission limitation, as compared to the previous assumption that utilities would perform 90 percent scrubbing on washed coal (resulting in more than 90 percent reduction in overall emissions). The agency’s analysis, according to EPA, showed that up to 22 percent of high sulfur coal reserves in the Eastern Midwest and parts of the Northern Appalachian coal regions would require more than 90 percent reduction if emissions were held to a 1.0 lbs./MBtu standard. Thus, although acknowledging that stricter controls were technically feasible, EPA chose to retain the 1.2 lbs./MBtu standard because “conservatism in utility perceptions of scrubber performance could create a significant disincentive against the use of these coals and disrupt the coal markets in these regions.” EPA concluded that “[a] more stringent emission limit would be counter to one of the basic purposes of the 1977 Amendments, that is, encouraging the use of higher sulfur coals.”

B. EDF’s Procedural Attack

EDF alleges that as a result of an “ex parte blitz” by coal industry advocates conducted after the close of the comment period, EPA backed away from adopting the .55 lbs./MBtu limit, and instead adopted the higher 1.2 lbs./MBtu restriction. EDF asserts that even before the comment period had ended EPA had already narrowed its focus to include only options which provided for the .55 lbs./MBtu ceiling. EDF also claims that as of March 9, 1979, the three proposals which EPA had under active consideration all included the more stringent .55 lbs./MBtu ceiling, and the earlier 1.2 lbs./MBtu ceiling had been discarded. Whether or not EDF’s scenario is credible, it is true that EPA did circulate a draft NSPS with an emissions ceiling below the 1.2 lbs./MBtu level for interagency comment during February, 1978. Following a “leak” of this proposal, EDF says, the so-called “ex parte blitz” began. “Scores” of pro-industry “ex parte” comments were received by EPA in the post-comment period, states EDF, and various meetings with coal industry advocates — including Senator Robert Byrd of West Virginia — took place during that period. These communications, EDF asserts, were unlawful and prejudicial to its position.

In order for this court to assess these claims, we must identify the particular actions and incidents which gave rise to EDF’s complaints. Aside from a passing reference to a telephone call from an EPA official to the Chief Executive Officer of NCA, EDF’s procedural objections stem from either (1) comments filed after the close of the official comment period, or (2) meetings between EPA officials and various government and private parties interested in the outcome of the final rule, all of which took place after the close of the comment period.

1. Late Comments

The comment period for the NSPS began on September 19, 1978, and closed on January 15, 1979. After January 15, EPA received almost 300 written submissions on the proposed rule from a broad range of interests. EPA accepted these comments and entered them all on its administrative docket. EPA did not, however, officially reopen the comment period, nor did it notify the public through the Federal Register or by other means that it had received and was entering the “late” comments. According to EDF, most of the approximately 300 late comments were received after the “leak” of the new .55 lbs./MBtu proposal. EDF claims that of the 138 late comments from non-government sources, at least 30 were from “representatives of the coal or utility industries,” and of the 53 comments from members of Congress, 22 were either forwarded by the Congressmen from industry interests, or else were prepared and submitted by Congressmen as advocates of those interests.

2. Meetings

EDF objects to nine different meetings. A chronological list and synopsis of the challenged meetings follows:

1. March 14, 1979 — This was a one and a half hour briefing at the White House for high-level officials from the Department of Energy (DOE), the Council of Economic Advisers (CEA), the White House staff, the Department of Interior, the Council on Environmental Quality (CEQ), the Office of Management and Budget (OMB), and the National Park Service. The meeting was reported in a May 9, 1979 memorandum from EPA to Senator Muskie’s staff, responding to the Senator’s request for a monthly report of contacts between EPA staff and other federal officials concerning the NSPS. A summary of the meeting and the materials distributed were docketed on May 30, 1979. EDF also obtained, after promulgation of the final rule, a copy of the memorandum to Senator Muskie in response to its Freedom of Information Act (“FOIA”) request.

2. April 5, 1979 — This is the meeting discussed at length above. The meeting was attended by representatives of EPA, DOE, NCA, EDF, Congressman Paul Simon’s office, ICF, Inc. (who performed the microanalysis), and Hunton & Williams (who represented the Electric Utilities). The participants were notified in advance of the agenda for the meeting. Materials relating to EPA’s and NCA’s presentations during the meeting were distributed and copies were later put into the docket along with detailed minutes of the meeting. Followup calls and letters between NCA and EPA came on April 20, 23, and 29, commenting or elaborating upon the April 5 data. All of these followup contacts were recorded in the docket

3. April 23, 1979 — This was a 30-45 minute meeting held at then Senate Majority Leader Robert Byrd’s request, in his office, attended by EPA Administrator Douglas Costle, Chief Presidential Assistant Stuart Eizenstat, and NCA officials. A summary of this meeting was put in the docket on May 1, 1979, and copies of the summary were sent to EDF and to other parties. In its denial of the petition for reconsideration, EPA was adamant that no new information was transmitted to EPA at this meeting.

4. April 27, 1979 — This was a briefing on dry scrubbing technology conducted by EPA for representatives of the Office of Science and Technology Policy, the Council on Wage and Price Stability, DOE, the President’s domestic policy staff, OMB, and various offices within EPA. A description of this briefing and copies of the material distributed were docketed on May 1, 1979.

5. April 30, 1979 — At 10:00 a. m., a one hour White House briefing was held for the President, the White House staff, and high ranking members of the Executive Branch “concerning the issues and options presented by the rulemaking.” This meeting was noted on an EPA official’s personal calendar which EDF obtained after promulgation in response to its FOIA request, but was never noted in the rulemaking docket.

6. April 30, 1979 — At 2:30 p. m., a technical briefing on dry scrubbing technology at the White House was conducted by EPA for the White House staff. A short memorandum describing this briefing was docketed on May 30, 1979.

7. May 1, 1979 — Another White House briefing was held on the subject of FGD technology. A description of the meeting and materials distributed were docketed on May 30, 1979.

8. May 1, 1979 — EPA conducted a one hour briefing of staff members of the Senate Committee on Environmental and Public Works concerning EPA’s analysis of the effect of alternative emission ceilings on coal reserves. The briefing was “substantially the same as the briefing given to Senator Byrd on May 2, 1980.” No persons other than Committee staff members and EPA officials attended the briefing.

This meeting, like the one at 10:00 a. m. on April 30, was never entered on the rulemaking docket but was listed on an EPA official’s calendar obtained by EDF in response to its FOIA request. This EPA official has since stated that it was an oversight not to have a memorandum of this briefing prepared for the docket.

9. May 2, 1979 — This was a brief meeting between Senator Byrd, EPA, DOE and NCA officials held ostensibly for Senator Byrd to hear EPA’s comments on the NCA data. A 49 word, not very informative, memorandum describing the meeting was entered on the docket on June 1, 1979.

On June 16, 1980, responding to motions filed by EDF, this court ordered EPA to file affidavits providing additional information regarding five of these nine meetings (March 14, April 23, April 27, April 30, and May 2, 1979). After EPA complied with the order, EDF argued that the other meetings held on April 30 and May 1 were still undocumented, whereupon EPA voluntarily filed an affidavit describing them.

EDF believes that the communications just outlined, when taken as a whole, were so extensive and had such a serious impact on the NSPS rulemaking, that they violated EDF’s rights to due process in the proceeding, and that these “ex parte” contacts were procedural errors of such magnitude that this court must reverse. EDF does not specify which particular features in each of the above-enumerated communications violated due process or constituted errors under the statute; indeed; EDF nowhere lists the communications in a form designed to clarify why any particular communication was unlawful. Instead, EDF labels all post-comment communications with EPA— from whatever source and in whatever form — as “ex parte,” and claims that “this court has repeatedly stated that ex parte contacts of substance violate due process.”

At the outset, we decline to begin our task of reviewing EPA’s procedures by labeling all post-comment communications with the agency as “ex parte.” Such an approach essentially begs the question whether these particular communications in an informal rulemaking proceeding were unlawful. Instead of beginning with a conclusion that these communications were “ex parte,” we must evaluate the various communications in terms of their timing, source, mode, content, and the extent of their disclosure on the docket, in order to discover whether any of them violated the procedural requirements of the Clean Air Act, or of due process.

C. Standard for Judicial Review of EPA Procedures

This court’s scope of review is delimited by the special procedural provisions of the Clean Air Act, which declare that we may reverse the Administrator’s decision for procedural error only if (i) his failure to observe procedural requirements was arbitrary and capricious, (ii) an objection was raised during the comment period, or the grounds for such objection arose only after the comment period and the objection is “of central relevance to the outcome of the rule,” and (iii) “the errors were so serious and related to matters of such central relevance to the rule that there is a substantial likelihood that the rule would have been significantly changed if such errors had not been made.” The essential message of so rigorous a standard is that Congress was concerned that EPA’s rulemaking not be casually overturned for procedural reasons, and we of course must respect that judgment.

Our authority to reverse informal administrative rulemaking for procedural reasons is also informed by Vermont Yankee Nuclear Power Corp. v. Natural Resources Defense Council, Inc. In its unanimous opinion, the Supreme Court unambiguously cautioned this court against imposing its own notions of proper procedures upon an administrative agency entrusted with substantive functions by Congress. The Court declared that so long as an agency abided by the minimum procedural requirements laid down by statute, this court was not free to impose additional procedural rights if the agency did not choose to grant them. Except in “extremely rare” circumstances, the Court stated, there is no justification for a reviewing court to overturn agency action because of the failure to employ procedures beyond those required by Congress.

[W]hen there is a contemporaneous explanation of the agency decision, the validity of that action must “stand or fall on the propriety of that finding, judged, of course, by the appropriate standard of review. If that finding is not sustainable on the administrative record made, then the . . . decision must be vacated and the matter remanded .. . for further consideration.” .... The [reviewing] court should engage in this kind of review and not stray beyond the judicial province to explore the procedural format or to impose upon the agency its own notion of which procedures are “best” and most likely to further some vague, undefined public good

Bearing this caveat in mind, we now set out the procedural requirements which Congress mandated for this rulemaking. Since EDF does not question — nor do we doubt— the constitutional sufficiency of the procedures mandated by the Clean Air Act, we shall reverse only (1) if the statutory requirements, or the procedures reasonably inferable from them or from basic notions of constitutional due process, were breached by EPA, and (2) where such breaches under the statute were “so serious and related to matters of such central relevance to the rule that there is a substantial likelihood that the rule would have been significantly changed if such errors had not been made.”

D. Statutory Provisions Concerning Procedure

The procedural provisions of the Clean Air Act specifying the creation and content of the administrative rulemaking record are contained in section 307. Responding in part to criticism that there was no formalized record which courts could rely upon when reviewing EPA rules,465 Congress enacted new procedures which represented “[b]y and large ... a legislative adoption of the suggestions for a rulemaking record set forth in a law review article dealing with EPA. (Pedersen, ‘Formal Records and Informal Rulemaking,’ 85 Yale L.J. 38 (1975)).” The Pedersen article argued for rules which would provide a reviewing court with a “procedural record” which it could rely upon when passing on agency rules. A “procedural record” is, according to Pedersen, a record defined by formal norms explicitly governing the inclusion and exclusion of data and which becomes a record “without further action.” “No inquiry [is] necessary [as] to whether the ‘agency’ actually had ‘considered’ the documents in the record, or whether they passed some test of relevance, anymore than is generally done in the course of appellate review of trial court decisions.” In this sense the Pedersen proposal for a “procedural record” in informal rulemaking resembles the records assembled in trial courts and agency formal adjudications, where record material is defined simply and exclusively as “material which has been accepted under a given obligatory set of procedures,” without regard to whether it was actually considered by the decisionmaker.

Pedersen distinguished his “procedural record” idea from what he called a “historical record” approach, in which a reviewing court requires the rulemaking agency to provide it with a post hoc assemblage of materials consisting of the data actually considered (as a matter of “historical” fact) by the agency decisionmaker, regardless of the procedures, if any, which governed the materials’ inclusion in any formal record. Pedersen criticized the “historical record” approach insofar as it affected the judicial review function, because (1) it confronted the courts with an “openended and disorganized” mass of evidence where “no one knows exactly what [the record should] consist of until judicial review is well underway,” and (2) it eroded the bar against probing the actual mental processes of the decisionmaker found in United States v. Morgan; since the “historical record” approach requires the court to decide what evidence “really” influenced the agency’s thinking. Pedersen’s reform proposal thus represented an explicit rejection of the “historical record” approach and was designed “to move rulemaking records as far as possible toward the ‘procedural’ end of the spectrum without reimposing the adjudicatory hearing requirements that have done so much damage in the past.”

Following Pedersen’s recommendations, the 1977 Amendments required the agency to establish a “rulemaking docket” for each proposed rule which would form the basis of the record for judicial review. The docket must contain, inter alia, (1) “notice of the proposed rulemaking . . . accompanied by a statement of its basis and purpose,” and a specification of the public comment period; (2) “all written comments and documentary information on the proposed rule received from any person . . . during the comment period[;] [t]he transcript of public hearings, if any[;] and [a]ll documents . .. which become available after the proposed rule has been published and which the Administrator determines are of central relevance to the rulemaking. . . .”; (3) drafts of proposed rules submitted for interagency review, and all documents accompanying them and responding to them; and (4) the promulgated rule and the various accompanying agency documents which explain and justify it.

In contrast to other recent statutes, there is no mention of any restrictions upon “ex parte” contacts. However, the statute apparently did envision that participants would normally submit comments, documentary material, and oral presentations during a prescribed comment period. Only two provisions in the statute touch upon the post-comment period, one of which, as noted immediately supra, states that “[a]ll documents which become available after the proposed rule has been published and which the Administrator determines are of central relevance to the rulemaking shall be placed in the docket as soon as possible after their availability.” But since all the post-comment period written submissions which EDF complains of were in fact entered upon the docket, EDF cannot complain that this provision has been violated.

The only other provision treating post-comment period procedures states that

Only an objection to a rule or procedure which was raised with reasonable specificity during the period for public comment (including any public hearing) may be raised during judicial review. If the person raising an objection can demonstrate to the Administrator that it was impracticable to raise such objection within such time or if the grounds for such objection arose after the period for public comment (but within the time specified for judicial review) and if such objection is of central relevance to the outcome of the rule, the Administrator shall convene a proceeding for reconsideration of the rule and provide the same procedural rights as would have been afforded had the information been available at the time the rule was proposed. If the Administrator refuses to convene such a proceeding, such person may seek review of such refusal in the United States court of appeals for the appropriate circuit. . . ,

In this case EPA refused to convene a reconsideration proceeding, stating

The Administrator does not believe that the procedures cited by EDF were improper. Moreover, as discussed below, any arguable errors were not of central relevance to the outcome of the rule, and therefore do not constitute grounds for granting EDF’s petition to reconsider.

Of course, if this assessment by EPA of EDF’s petition for reconsideration were wrong, it would constitute reversible error. But since this court can reverse an agency on procedural grounds only if it finds a failure to observe procedures “required by law,” we must first decide whether the procedures followed by EPA between January 15 and June 1, 1979 were unlawful. Only if we so find would we then face the second issue whether the unlawful errors were “of such central relevance to the rule that there is a substantial likelihood that the rule would have been significantly changed if such errors had not been made.” We now hold that EPA’s procedures during the post-comment period were lawful, and therefore do not face the issue whether any alleged errors were of “central relevance” to the outcome.

E. Validity of EPA’s Procedures During the Post-Comment Period

The post-comment period communications about which EDF complains vary widely in their content and mode; some are written documents or letters, others are oral conversations and briefings, while still others are meetings where alleged political arm-twisting took place. For analytical purposes we have grouped the communications into categories and shall discuss each of them separately. As a general matter, however, we note at the outset that nothing in the statute prohibits EPA from admitting all post-comment communications into the record; nothing expressly requires it, either. Most likely the drafters envisioned promulgation of a rule soon after the close of the public comment period, and did not envision a months-long hiatus where continued outside communications with the agency would continue unabated. We must therefore attempt to glean the law for this case by inference from the procedural framework provided in the statute.

1. Written Comments Submitted During Post-Comment Period

Although no express authority to admit post-comment documents exists, the statute does provide that:

All documents which become available after the proposed rule has been published and which the Administrator determines are of central relevance to the rulemaking shall be placed in the docket as soon as possible after their availability.

This provision, in contrast to others in the same subparagraph, is not limited to the comment period. Apparently it allows EPA not only to put documents into the record after the comment period is over, but also to define which documents are “of central relevance” so as to require that they be placed in the docket. The principal purpose of the drafters was to define in advance, for the benefit of reviewing courts, the record upon which EPA would rely in defending the rule it finally adopted; it was not their purpose to guarantee that every piece of paper or phone call related to the rule which was received by EPA during the post-comment period be included in the docket. EPA thus has authority to place post-comment documents into the docket, but it need not do so in all instances.

Such a reading of the statute accords well with the realities of Washington administrative policymaking, where rumors, leaks, and overreactions by concerned groups abound, particularly as the time for promulgation draws near. In a proceeding such as this, one of vital concern to so many interests — industry, environmental groups, as well as Congress and the Administration — it would be unrealistic to think there would not naturally be attempts on all sides to stay in contact with EPA right up to the moment the final rule is promulgated. The drafters of the 1977 Amendments were practical people, well versed in such activity, and we decline now to infer from their silence that they intended to prohibit the lodging of documents with the agency at any time prior to promulgation. Common sense, after all, must play a part in our interpretation of these statutory procedures.

EPA of course could have extended, or reopened, the comment period after January 15 in order formally to accommodate the flood of new documents; it has done so in other cases. But under the circumstances of this case, we do not find that it was necessary for EPA to reopen the formal comment period. In the first place, the comment period lasted over four months, and although the length of the comment period was not specified in the 1977 Amendments, the statute did put a premium on speedy decisionmaking by setting a one year deadline from the Amendments’ enactment to the rules’ promulgation. EPA failed to meet that deadline, and subsequently entered into a consent decree where it promised to adopt the final rules by March 19, 1979, over seven months late. EPA also failed to meet that deadline, and it was once more extended until June 1, 1979 upon agreement of the parties pursuant to court order. Reopening the formal comment period in the late spring of 1979 would have confronted the agency with a possible violation of the court order, and would further have frustrated the Congressional intent that these rules be promulgated expeditiously.

If, however, documents of central importance upon which EPA intended to rely had been entered on the docket too late for any meaningful public comment prior to promulgation, then both the structure and spirit of section 307 would have been violated. The Congressional drafters, after all, intended to provide “thorough and careful procedural safeguards . .. [to] insure an effective opportunity for public participation in the rulemaking process.” Indeed the Administrator is obligated by the statute to convene a proceeding to reconsider the rule where an objection of central importance to it is proffered, and the basis of the objection arose after the comment period had closed. Thus we do not hold that there are no circumstances in which reopening the comment period would ever be required.

The case before us, however, does not present an instance where documents vital to EPA’s support for its rule were submitted so late as to preclude any effective public comment. The vast majority of the written comments referred to earlier at text accompanying nn.425 — 27, supra, were submitted in ample time to afford an opportunity for response. Regarding those documents submitted closer to the promulgation date, our review does not reveal that they played any significant role in the agency’s support for the rule. The decisive point, however, is that EDF itself has failed to show us any particular document or documents to which it lacked an opportunity to respond, and which also were vital to EPA’s support for the rule.

EDF makes only one particularized allegation concerning its inability to respond adequately to documents submitted during the post-comment period. It argues that at the April 5 meeting called by EPA, representatives of NCA produced new data purporting to show a significant impact upon available coal reserves of more restrictive emissions ceilings. EDF alleges that additional documents supporting a higher ceiling were thereafter forwarded by NCA to EPA following the April 5 meeting. We find, however, that EDF was not denied an adequate opportunity to respond to this material. EDF was provided with advance notice of the April 5 meeting’s time, place, and agenda. At the meeting EDF proceeded to question the assumptions used in the coal industry’s studies. After the meeting, on April 19, 1979, it sent a detailed memorandum to EPA asserting that NCA’s new claims were “false” and “unsupported by the sheafs of new data the Coal Association has hastened to submit....” Of course EDF would have preferred “additional time” to be able to furnish a “more complete evaluation” of the studies, but we do not find that EDF’s preference for more time constitutes substantial evidence of an inability to respond. EDF had many weeks between the meeting and the promulgation of the rule to submit additional material, and its rebuttal material has all been entered on the docket and considered by EPA. The mere wishes of a participant in an informal rulemaking for more time to respond to documents in the record to which it already had opportunity to respond cannot force an agency to delay rulemaking simply because some new rebuttal evidénce may be forthcoming; this is particularly so when the statute mandates speedy promulgation of the rule. Were it otherwise, participants could delay promulgation indefinitely since new information continually comes to light on the subject of many proposed rules. Finality, after all, has a place in administrative rulemaking, just as it does in judicial decisionmaking.

We therefore conclude that it was not improper in this case for EPA to docket and consider the post-comment documents submitted to it. Nor was it improper for EPA to decline to reopen the formal comment period and delay promulgation, since there was no proof that evidence crucial to the rule’s validity was entered too late for any effective public comment.

2. Meetings Held With Individuals Outside EPA

The statute does not explicitly treat the issue of post-comment period meetings with individuals outside EPA. Oral face-to-face discussions are not prohibited anywhere, anytime, in the Act. The absence of such prohibition may have arisen from the nature of the informal rulemaking procedures Congress had in mind. Where agency action resembles judicial action, where it involves formal rulemaking, adjudication, or quasi-adjudication among “conflicting private claims to a valuable privilege,” the insulation of the decisionmaker from ex parte contacts is justified by basic notions of due process to the parties involved. But where agency action involves informal rulemaking of a policymaking sort, the concept of ex parte contacts is of more questionable utility.

Under our system of government, the very legitimacy of general policymaking performed by unelected administrators depends in no small part upon the openness, accessibility, and amenability of these officials to the needs and ideas of the public from whom their ultimate authority derives, and upon whom their commands must fall. As judges we are insulated from these pressures because of the nature of the judicial process in which we participate; but we must refrain from the easy temptation to look askance at all face-to-face lobbying efforts, regardless of the forum in which they occur, merely because we see them as inappropriate in the judicial context. Furthermore, the importance to effective regulation of continuing contact with a regulated industry, other affected groups, and the public cannot be underestimated. Informal contacts may enable the agency to win needed support for its program, reduce future enforcement requirements by helping those regulated to anticipate and shape their plans for the future, and spur the provision of information which the agency needs. The possibility of course exists that in permitting ex parte communications with rulemakers we create the danger of “one administrative record for the public and this court and another for the Commission.” Under the Clean Air Act procedures, however, “[t]he promulgated rule may not be based (in part or whole) on any information or data which has not been placed in the docket.. . .” Thus EPA must justify its rulemaking solely on the basis of the record it compiles and makes public.

Regardless of this court’s views on the need to restrict all post-comment contacts in the informal rulemaking context, however, it is clear to us that Congress has decided not to do so in the statute which controls this case. As we have previously noted:

Where Congress wanted to prohibit ex parte contacts it clearly did so. Thus APA § 5(c) forbids ex parte contacts when an “adjudication” is underway, but even that prohibition does not apply to “the agency or a member or members of the body comprising the agency.” 5 U.S.C. § 554(d)(C) (1970).... If Congress wanted to forbid or limit ex parte contact in every case of informal rule-making, it certainly had a perfect opportunity of doing so when it enacted the Government in the Sunshine Act, Pub.L. No. 94-409, 90 Stat. 1241 (Sept. 13, 1976).... That it did not extend the ex parte contact provisions of the amended section 557 to section 553 — even though such an extension was urged upon it during the hearing — is a sound indication that Congress still does not favor a per se prohibition or even a “logging” requirement in all such proceedings.

Lacking a statutory basis for its position, EDF would have us extend our decision in Home Box Office, Inc. v. FCC to cover all meetings with individuals outside EPA during the post-comment period. Later decisions of this court, however, have declined to apply Home Box Office to informal rule-making of the general policymaking sort involved here, and there is no precedent for applying it to the procedures found in the Clean Air Act Amendments of 1977.

It still can be argued, however, that if oral communications are to be freely permitted after the close of the comment period, then at least some adequate summary of them must be made in order to preserve the integrity of the rulemaking docket, which under the statute must be the sole repository of material upon which EPA intends to rely. The statute does not require the docketing of all post-comment period conversations and meetings, but we believe that a fair inference can be drawn that in some instances such docketing may be needed in order to give practical effect to section 307(d)(4)(B)(i), which provides that all documents “of central relevance to the rulemaking” shall be placed in the docket as soon as possible after their availability. This is so because unless oral communications of central relevance to the rulemaking are also docketed in some fashion or other, information central to the justification of the rule could be obtained without ever appearing on the docket, simply by eommunicáting it by voice rather than by pen, thereby frustrating the command of section 307 that the final rule not be “based (in part or whole) on any information or data which has not been placed in the docket. . . .”

EDF is understandably wary of a rule which permits the agency to decide for itself when oral communications are of such central relevance that a docket entry for them is required. Yet the statute itself vests EPA with discretion to decide whether “documents” are of central relevance and therefore must be placed in the docket; surely EPA can be given no less discretion in docketing oral communications, concerning which the statute has no explicit requirements whatsoever. Furthermore, this court has already recognized that the relative significance of various communications to the outcome of the rule is a factor in determining whether their disclosure is required. A judicially imposed blanket requirement that all post-comment period oral communications be docketed would, on the other hand, contravene our limited powers of review, would stifle desirable experimentation in the area by Congress and the agencies, and is unnecessary for achieving the goal of an established, procedure-defined docket, viz., to enable reviewing courts to fully evaluate the stated justification given by the agency for its final rule.

Turning to the particular oral communications in this case, we find that only two of the nine contested meetings were undocketed by EPA. The agency has maintained that, as to the May 1 meeting where Senate staff people were briefed on EPA’s analysis concerning the impact of alternative emissions ceilings upon coal reserves, its failure to place a summary of the briefing in the docket was an oversight. We find no evidence that this oversight was anything but an honest inadvertence; furthermore, a briefing of this sort by EPA which simply provides background information about an upcoming rule is not the type of oral communication which would require a docket entry under the statute.

The other undocketed meeting occurred at the White House and involved the President and his White House staff. Because this meeting involves considerations unique to intra-executive meetings, it is discussed in the section immediately infra.

(a) Intra-Executive Branch Meetings

We have already held that a blanket prohibition against meetings during the posicomment period with individuals outside EPA is unwarranted, and this perforce applies to meetings with White House officials. We have not yet addressed, however, the issue whether such oral communications with White House staff, or the President himself, must be docketed on the rulemaking record, and we now turn to that issue. The facts, as noted earlier, present us with a single undocketed meeting held on April 30, 1979, at 10:00 a. m., attended by the President, White House staff, other high ranking members of the Executive Branch, as well as EPA officials, and which concerned the issues and options presented by the rulemaking.

We note initially that section 307 makes specific provision for including in the rulemaking docket the “written comments” of other executive agencies along with accompanying documents on any proposed draft rules circulated in advance of the rulemaking proceeding. Drafts of the final rule submitted to an executive review process prior to promulgation, as well as all “written comments,” “documents,” and “written responses” resulting from such interagency review process, are also to be put in the docket prior to promulgation. This specific requirement does not mention informal meetings or conversations concerning the rule which are not part of the initial or final review processes, nor does it refer, to oral comments of any sort. Yet it is hard to believe Congress was unaware that intra-executive meetings and oral comments would occur throughout the rulemaking process. We assume, therefore, that unless expressly forbidden by Congress, such intra-executive contacts may take place, both during and after the public comment period; the only real issue is whether they must be noted and summarized in the docket.

The court recognizes the basic need of the President and his White House staff to monitor the consistency of executive agency regulations with Administration policy. He and his White House advisers surely must be briefed fully and frequently about rules in the making, and their contributions to policymaking considered. The executive power under our Constitution, after all, is not shared — it rests exclusively with the President. The idea of a “plural executive,” or a President with a council of state, was considered and rejected by the Constitutional Convention. Instead the Pounders chose to risk the potential for tyranny inherent in placing power in one person, in order to gain the advantages of accountability fixed on a single source. To ensure the President’s control and supervision over the Executive Branch, the Constitution — and its judicial gloss — vests him with the powers of appointment and removal, the power to demand written opinions from executive officers, and the right to invoke executive privilege to protect consultative privacy. In the particular case of EPA, Presidential authority is clear since it has never been considered an “independent agency,” but always part of the Executive Branch.

The authority of the President to control and supervise executive policymaking is derived from the Constitution; the desirability of such control is demonstrable from the practical realities of administrative rulemaking. Regulations such as those involved here demand a careful weighing of cost, environmental, and energy considerations. They also have broad implications for national economic policy. Our form of government simply could not function effectively or rationally if key executive policymakers were isolated from each other and from the Chief Executive. Single mission agencies do not always have the answers to complex regulatory problems. An overworked administrator exposed on a 24-hour basis to a dedicated but zealous staff needs to know the arguments and ideas of policymakers in other agencies as well as in the White House.

We recognize, however, that there may be instances where the docketing of conversations between the President or his staff and other Executive Branch officers or rulemakers may be necessary to ensure due process. This may be true, for example, where such conversations directly concern the outcome of adjudications or quasi-adjudicatory proceedings; there is no inherent executive power to control the rights of individuals in such settings. Docketing may also be necessary in some circumstances where a statute like this one specifically requires that essential “information or data” upon which a rule is based be docketed. But in the absence of any further Congressional requirements, we hold that it was not unlawful in this case for EPA not to docket a face-to-face policy session involving the President and EPA officials during the post-comment period, since EPA makes no effort to base the rule on any “information or data” arising from that meeting. Where the President himself is directly involved in oral communications with Executive Branch officials, Artiele II considerations — combined with the strictures of Vermont Yankee — require that courts tread with extraordinary caution in mandating disclosure beyond that already required by statute.

The purposes of full-record review which underlie the need for disclosing ex parte conversations in some settings do not require that courts know the details of every White House contact, including a Presidential one, in this informal rulemaking setting. After all, any rule issued here with or without White House assistance must have the requisite factual support in the rulemaking record, and under this particular statute the Administrator may not base the rule in whole or in part on any “information or data” which is not in the record, no matter what the source. The courts will monitor all this, but they need not be omniscient to perform their role effectively. Of course, it is always possible that undisclosed Presidential prodding may direct an outcome that is factually based on the record, but different from the outcome that would have obtained in the absence of Presidential involvement. In such a case, it would be true that the political process did affect the outcome in a way the courts could not police. But we do not believe that Congress intended that the courts convert informal rulemaking into a rarified technocratic process, unaffected by political considerations or the presence of Presidential power. In sum, we find that the existence of intra-Executive Branch meetings during the post-comment period, and the failure to docket one such meeting involving the President, violated neither the procedures mandated by the Clean Air Act nor due process.

(b) Meetings Involving Alleged Congressional Pressure

Finally, EDF challenges the rulemaking on the basis of alleged Congressional pressure, citing principally two meetings with Senator Byrd. EDF asserts that under the controlling case law the political interference demonstrated in this case represents a separate and independent ground for invalidating this rulemaking. But among the cases EDF cites in support of its position, only D. C. Federation of Civil Associations v. Volpe seems relevant to the facts here.

In D. C. Federation the Secretary of Transportation, pursuant to applicable federal statutes, made certain safety and environmental findings in designating a proposed bridge as part of the interstate highway system. Civic associations sought to have these determinations set aside for their failure to meet certain statutory standards, and because of possible tainting by reason of improper Congressional influence. Such influence chiefly included public statements by the Chairman of the House Subcommittee on the District of Columbia, Representative Natcher, indicating in no uncertain terms that money earmarked for the construction of the District of Columbia’s subway system would be withheld unless the Secretary approved the bridge. While a majority of this court could not decide whether Representative Natcher’s extraneous pressure had in fact influenced the Secretary’s decision, a majority did agree on the controlling principle of law: “that the decision [of the Secretary] would be invalid if based in whole or in part on the pressures emanating from Representative Natcher.” In remanding to the Secretary for new determinations concerning the bridge, however, the court went out of its way to “emphasize that we have not found — nor, for that matter, have we sought — any suggestion of impropriety or illegality in the actions of Representative Natcher and others who strongly advocate the bridge.” The court remanded simply so that the Secretary could make this decision strictly and solely on the basis of considerations made relevant by Congress in the applicable statute.

D. C. Federation thus requires that two conditions be met before an administrative rulemaking may be overturned simply on the grounds of Congressional pressure. First, the content of the pressure upon the Secretary is designed to force him to decide upon factors not made relevant by Congress in the applicable statute. Representative Natcher’s threats were of precisely that character, since deciding to approve the bridge in order to free the “hostage” mass transit appropriation was not among the decisionmaking factors Congress had in mind when it enacted the highway approval provisions of Title 23 of the United States Code. Second, the Secretary’s determination must be affected by those extraneous considerations.

In the case before us, there is no persuasive evidence that either criterion is satisfied. Senator Byrd requested a meeting in order to express “strongly” his already well-known views that the SO2 standards’ impact on coal reserves was a matter of concern to him. EPA initiated a second responsive meeting to report its reaction to the reserve data submitted by the NCA. In neither meeting is there any allegation that EPA made any commitments to Senator Byrd. The meetings did underscore Senator Byrd’s deep concerns for EPA, but there is no evidence he attempted actively to use “extraneous” pressures to further his position. Americans rightly expect their elected representatives to voice their grievances and preferences concerning the administration of our laws. We believe it entirely proper for Congressional representatives vigorously to represent the interests of their constituents before administrative agencies engaged in informal, general policy rulemaking, so long as individual Congressmen do not frustrate the intent of Congress as a whole as expressed in statute, nor undermine applicable rules of procedure. Where Congressmen keep their comments focused on the substance of the proposed rule — and we have no substantial evidence to cause us to believe Senator Byrd did not do so here — administrative agencies are expected to balance Congressional pressure with the pressures emanating from all other sources. To hold otherwise would deprive the agencies of legitimate sources of information and call into question the validity of nearly every controversial rule-making. * * * * * #

In sum, we conclude that EPA’s adoption of the 1.2 lbs./MBtu emissions ceiling was free from procedural error. The post-comment period contacts here violated neither the statute nor the integrity of the proceeding. We. also hold that it was not improper for the agency to docket and consider documents submitted to it during the post-comment period, since no document vital to EPA’s support for the rule was submitted so late as to preclude any effective public comment. Hence we find no reason under section 307 to overturn the 1.2 lbs./MBtu standard. The field of course is open for Congress or the agency to formulate further procedural rules in this area.

CONCLUSION

Since the issues in this proceeding were joined in 1973 when the Navajo Indians first complained about sulfur dioxide fumes over their Southwest homes, we have had several lawsuits, almost four years of substantive and procedural maneuvering before the EPA, and now this extended court challenge. In the interim, Congress has amended the Clean Air Act once and may be ready to do so again. The standard we uphold has already been in effect for almost two years, and could be revised within another two years.

We reach our decision after interminable record searching (and considerable soul searching). We have read the record with as hard a look as mortal judges can probably give its thousands of pages. We have adopted a simple and straight-forward standard of review, probed the agency’s rationale, studied its references (and those of appellants), endeavored to understand them where they were intelligible (parts were simply impenetrable), and on close questions given the agency the benefit of the doubt out of deference for the terrible complexity of its job. We are not engineers, computer modelers, economists or statisticians, although many of the documents in this record require such expertise — and more.

Cases like this highlight the critical responsibilities Congress has entrusted to the courts in proceedings of such length, complexity and disorder. Conflicting interests play fiercely for enormous stakes, advocates are prolific and agile, obfuscation runs high, common sense correspondingly low, the public interest is often obscured.

We cannot redo the agency’s job; Congress has told us, at least in proceedings under this Act, that it will not brook reversal for small procedural errors; Vermont Yankee reinforces the admonition. So in the end we can only make our best effort to understand, to see if the result makes sense, and to assure that nothing unlawful or irrational has taken place. In this case, we have taken a long while to come to a short conclusion: the rule is reasonable.

Affirmed.

ROBB, Circuit Judge, concurs in the result.

APPENDIX

Figure 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 Description Typical Wet Scrubber Typical Dry Scrubber Typical Dry Scrubber EPA Phase Three Modeling Analysis, Table 1 EPA Phase Three Modeling Analysis, Table 2 EPA Phase Three Modeling Analysis, Table 3 EPA Phase Three Modeling Analysis, Table 4 EPA Phase Three Modeling Analysis, Table 5 EPA Reconsideration Analysis, Table 1 EPA Reconsideration Analysis, Table 2 EPA Reconsideration Analysis, Table 3 EPA Economic Analysis of Dry Scrubbing EPA Economic Analysis of Dry Scrubbing EPA Economic Analysis of Dry Scrubbing EPA Economic Analysis of Dry Scrubbing EPA Economic Analysis of Dry Scrubbing EPA Economic Analysis of Dry Scrubbing EPA Economic Analysis of Dry Scrubbing Typical ESP Typical Baghouse (2 Cell) Typical Baghouse (Multicell) EPA’s ESP Data EPA’s ESP Data for Difficult Cases EPA’s Baghouse Data

Ad. Doc. No. III-B-3, supra note 9, at 4-77, J.A. at 1863.

Figure 2 — Flow Sheet — Two Stage Dry Scrubber/S02 Absorber

Ad. Doc. No. III-B-3, supra note 9, at 4-131, J.A. at 1917.

Figure 3

Antelope Valley Station Flow Diagram

Figure 4

Figure 5

a Results of joint EPA/DOE analyses completed in May 1979 based on oil prices of $12.90, $16.40, and $21.00/bbl in the years 1985, 1990, and 1995, respectively.

b With 520 ng/J maximum emission limit.

“Plants subject to existing State regulations or the current NSPS of 1.2 lb S02/million BTU.

4 Based on wet SO, scrubbing costs.

8 Based on dry S02 scrubbing costs where applicable.

f Plants subject to the revised standards.

44 Fed. Reg. at 33608.

Figure 6

a Results of joint EPA/DOE analyses completed in May 1979 based on oil prices of $12.90, $16.40, and $21.00/bbl in the years 1985, 1990, and 1995, respectively.

b With 520 ng/J maximum emission limit.

® Based on wet S02 scrubbing costs.

d Based on dry S02 scrubbing costs where applicable.

® New England, Middle Atlantic, South Atlantic, and East South Central Census Regions.

f East North Central and West North Central Census Region. .

e West South Central Census Region,

h Mountain and Pacific Census Regions.

44 Fed. Reg. at 33608.

Figure 7

a Results of EPA analyses completed in May 1979 based on oil prices of $12.90, $16.40, and $21.00/bbl in the years 1985, 1990, and 1995, respectively.

b With 520ng/J maximum emission limit.

c Based on wet SO? scrubbing costs.

<* * Based on dry S02 scrubbing where applicable.

44 Fed. Reg. at 33609.

Figure 8

a Results of EPA analyses completed in May 1979 based on oil prices of $12.90, $16.40, and $21.00/bbl in the years 1985, 1990, and 1995, respectively.

b With 520 ng/J maximum emission limit

c Based on wet S02 scrubbing costs.

* Based on dry S02 scrubbing costs where applicable.

44 Fed. Reg. at 33609.

Figure 9

1 With wet and dry scrubbing and the following energy assumptions:

Figure 10

iWith wet and dry scrubbing and the following energy assumptions:

2 See 44 FR 33608 for designation of census regions.

45 Fed. Reg. at 8219.

Figure 11

1 With wet and dry scrubbing and the following energy assumptions:

2 See 44 FR 33608 to designation of census regions.

45 Fed. Reg. at 8219.

Figure 12 — Percent S02 Removal and Stoichiometric for Alkaline Ash Coals6

Ad. Doc. No. V-B-l, supra note 75, at 3-65, J.A. at 2669.

Figure 13

Ad. Doc. No. V-B-l, supra note 75, at 3-67, J.A. at 2671.

Figure 14

Ad. Doc. No. V-B-l, supra note 75, at 3-69, J.A. at 2673.

Figure 15 — Economic Comparison Between Wet and Dry FGD Processes at 70% S02 Removal (Alkaline Ash)

Ad. Doc. No. V-B-l, supra note 75, at 3-70, J.A. at 2674.

Figure 16 — Economic Comparison Between Wet and Dry FGD Processes at 70% S02 Removal (Non-Alkaline Ash)

Ad. Doc. No. V-B-l, swpra note 75, at 3-71, J.A. at 2675.

Figure 17 — Economic Comparison Between Wet and Dry FGD Processes at 80% Removal (Non-Alkaline Ash)

Ad. Doc. No. V-B-l, supra note 75, at 3-72, J.A. at 2676.

Figure 18 — Uncertainty in Economic Comparisons At 70% S02 Removal

Ad. Doc. No. V-B-l, swpra note 75, at 3-74, J.A. at 2678.

Figure 20 — A Simple Two Cell Inside Out Baghouse

Ad. Doc. No. III-B-1, swpra note 311, at 4-12, J.A. at 1372.

Figure 2.1 — Exterior View of a Multicell Baghouse with One Cell Removed

FIGURE 22

Table 4-2 — Summary of Data on Pulverized Coal-Fired Steam Generator High Efficiency Electrostatic Precipitator Systems — Continued Unit & Reference Identification Number Unit Size ESP Type Megawatts (•# Sulfur) Specific Collection Area (SCA) Square Metres Per Actual Cubic Metres per Second (Ft2/1000 ACFM) Control Effectiveness Nanograms per Joule (lb/106 Btu) 1218 1318 141® 1520 1621 1722 1822 1923 2024 2128 250 250 190 350 700 141 187 411 74 680 Cold(0.7) Cold (0.7) Hot(1.4) Hot (0.4) Hot(1.4) NG(0.8) NG(0.8) NG(l.l) NG(1.4) Cold (0.5) 158 (803) 158 (803) 53.0 (269) NG 53.7 (273) NG NG NG NG 151.0 (767) 19- 20 (0.044-0.047) 20- 21 (0.046-0.050) 4.3-5.6a (.010-.013) 18.9®.* (0.044) 15-17“.* (.034-.039) 11- 13“ (.026-.030) 6.0-7.3® (0.014-.017) 5.6-10“ (.013-.024) 10.13“ (.024-.031) 12- 17“.* (0.027-0.040)

“EPA Method 5

* EPA Sponsored Test

NG = Data not given

Ad. Doc. No. III-B-1, supra note 311, at 4-34, J.A. at 1394.

Figure 23

Table 4-3 — Summary of Data on Difficult Electrostatic Precipitator Control Cases for Pulverized Coal-Fired Steam Generators Unit & Reference Identification Number Unit Size ESP Type Megawatts (% Sulfur) Specific Collection Area (SCA) Square Metres Per Actual Cubic Metres per Second (FtVIOOO ACFM) Average Control Effectiveness Nanograms per Joule (lb/106 Btu) 2io 310 2226 1218 1318 613 2128 800 800 330 250 250 500 680 Hot(0.5) Hot(0.5) Hot(0.9) Cold (0.7) Cold (0.7) • Cold (0.5) Cold (0.5) 60.4 (307) 60.4 (307) 57.5 (292) 158 (803) 158 (803) 174 (884) 151 (767) 13.7“ (0.032) 15.5“ (0.036) 17.2“ (0.040) 19.8 (0.046) 20.6 (0.048) 4.0“ (0.0094) 13.6 (0.032)

“ = EPA Method 5

* = EPA Sponsored Test

Ad. Doc. No. III-B-1, supra note 311, at 4-38, J.A. at 1398.

Figure 24

Table 4-5 — Summary of Data on Baghouses Applied to Coal-Fired Steam Generator Combustion Gases Air to Cloth Ratio Coal Sulfur Actual Cubic Metres Effectiveness Source Content and Type Per Minute per Pressure Drop Nanograms Identification Source Source Size Type Cleaning Square Metre Kilopascals per Joule Number_Type Megawatts Filtration Method (ACFM/Ft2)_(inches H,Q) (lb/lQs Btu) S(2.0) V* * S(2.0) 22» PC (2.0) 38» S (0.7) 48» s 580 g 68» S 78« s 888 PC(0.5) xo* 10* 44** 13** 18* 12.5* 24* 6.4* 25* Outside-in Outside-in Inside-out Inside-out NG NG NG NG Inside-out Reverse air Pulse jet Reverse air Shaking and reverse air NG NG NG NG Reverse air 0.61-0.76 (2.0-2.5) 0.76-0.91 (2.5-3.0) 0.58 (1.9) 0.85 (2.8) NG NG NG NG 0.69 (2.26) 0.52-0.70 (2.1-2.8) 0.55-1.1 (2.2-4.3) 0.62 (2.5) 1.25 (5.0) NG NG NG NG 2-2.5 (8-10) 4.7a*b (0.011) 9.9a«b (0.023) I. 2-43*.»» (0.0028-0.0100) 0.60-7.7a*b (0.0014-0.0180) II. 2* (0.026) 3.9* (0.0.009) 18* (0.042) 6.4* (0.015) 15.5*.*» (0.036)

NG = Data not given » = EPA Method 5

S = Stoker b — EPA Sponsored Test

PC = Pulverized Coal 0 = Non-EPA or No Data

* = Industrial Boiler ** = Utility Boiler

Ad. Doc. No. III-B-1, supra note 311, at 4-41, J.A. at 1401. 
      
      . 42 U.S.C. § 7401 et seq. (1979 Supp. III) (“Clean Air Act” or “Act”). The original Clean Air Act, Pub.L.No. 84-159, 69 Stat. 322 (1955), has been amended numerous times since its initial passage. The term “Clean Air Act” or “Act” will be used in text and notes to refer to the version of the Act contextually relevant at that point in the opinion. [Hereinafter citations to current code will omit date.]
     
      
      . 42 U.S.C. § 7411(a) & (b).
     
      
      . 44 Fed.Reg. 33580 (June 11, 1979). [Citations to Federal Register will omit date after first citation.]
     
      
      . The NSPS apply to all fossil-fuel fired generators but the standards are only challenged here so far as they relate to coal-fired generators.
     
      
      . The standard of performance restricting the emission of nitrogen oxide is not before the court.
     
      
      . MBtu refers to Million British thermal units which is a measure of heat energy. A single Btu is the amount of energy required to raise the temperature of one pound of water one degree Fahrenheit. This measure is appropriate here because utility plants combust coal to heat water which produces steam used for generating electricity.
      The NSPS apply to units capable of firing greater than 250 MBtu per hour. (A boiler capable of burning 250 MBtu per hour can consume approximately ten tons of coal per hour, or about one railroad car of coal (70 tons) every seven hours.) A typical 500 megawatt (MW) power plant can bum about 5000 MBtu per hour. At full capacity it would consume 200 tons of coal per hour or one railroad car every twenty minutes. Brief for Respondent EPA at 8 n.6.
      “lbs./MBtu” is a ratio of the weight of emissions to the heat content of the fuel. (Different coals have different heat content.) At 1.2 pounds per MBtu, a boiler with 250 MBtu capacity would emit 300 pounds of sulfur dioxide per hour. The consumption of a ton of coal, at 25 MBtu’s a ton heat content, would emit 30 pounds of sulfur dioxide to the atmosphere. Brief for Respondent EPA at 8 n.7.
     
      
      . “ng/j” refers to nanogram per joule which is the alternative measure in the metric system of the ratio of emissions to heat input.
     
      
      . The significance of this case is reflected to some degree in a spate of recent articles. See Ackerman & Hassler, Beyond the New Deal: Coal and the Clean Air Act, 89 Yale L.J. 1466 (1980). Ackerman and Hassler’s article appears in expanded form as a book entitled Clean Coal/Dirty Air: or How the Clean Air Act Became a Multibillion-Dollar Bail-Out for High Sulfur Coal Producers and What Should Be Done About It (Yale Univ. Press 1981); Banks, EPA Bends to Industry Pressure on Coal NSPS — and Breaks, 9 Ecology L.Q. 67 (1980) ; Currie, Direct Federal Regulation of Stationary Sources Under the Clean Air Act, 128 U.Pa.L.Rev. 1389 (1980); Navarro, The Politics of Air Pollution, Public Interest, Spring 1980, 36-44; see also New Source Performance Standards for Coal-Fired Power Plants, 8 Ecology L.Q. 784 (1980); Reconciling Coal Conversion Policy and Significant Deterioration of Air Quality, 15 Tulsa L.J. 532 (1980).
      
        See generally Report of the National Commission on Air Quality, To Breathe Clean Air (1981) ; Del Duca, The Clean Air Act: A Realistic Assessment of Cost Effectiveness, 5 Harv. Env.L.Rev. 184 (1981); Harrison & Portney, Making Ready for the Clean Air Act, Regulation, March/April 1981, 24-31; Smith, The Fight Over Clean Air Begins, SCIENCE, March 20, 1981, 1328-30.
     
      
      . See “The Electric Power Industry in the United States,” Background Information for Proposed SO2 Emission Standards, 5-2, J.A. 1753, 1940 (EPA Pub.No. 450/2-78-007a July 1978) (Ad.Doc.No. III-B-3). [After first full citation documents in the administrative record will be cited by their administrative docket number “Ad.Doc.No.” with a reference back to the place in the opinion where the full citation occurs, followed by parallel citations to the original page numbers, and the Joint Appendix page numbers “J.A.” Thus, the above cited document will hereinafter appear as Ad. Doc.No. III-B-3, supra note 9, at 5-2, J.A. at 1940.]
      In 1976 coal-fired steam turbine generators made up 38 percent of the total generating capacity installed in the United States, far more than any other type of generators. Approximately 46.3 percent of the total net production of electrical energy in the United States in 1976 was derived from coal. Id. at 5-2 to 5-3, J.A. at 1940-41. By 1979 coal burning power plants contributed 48 percent of all electrical power produced in the United States. Ackerman & Hassler, supra note 8, at 1468 (citing 2 U.S. Energy Information Admin., Ann.Rep. to Congress 135 (1979)). During 1980, 830 million tons of coal were mined and electric utilities consumed 565 million tons. Taylor, Coal: Buried Under Tons of Problems, U.S. News & World Report, April 16, 1981 at 57-58.
     
      
      . “EPA News Release Announcing Final Standards” 1, 3, J.A. 3129, 3131 (EPA, May 25, 1979) (Ad.Doc.No. V-C-2); Department of Health, Education, and Welfare, Air Quality Criteria for Particulate Matter, AP — 49 (1969); Department of Health, Education, and Welfare, Air Quality Criteria for Sulfur Oxides, AP-50 (1970).
     
      
      . 44 Fed.Reg. at 33608, Table 2 (Figure 5 in the appendix to this opinion). While the figures in Table 2 show a 27 percent increase, EPA projected only a 17 percent increase in national sulfur dioxide emissions in the text of the preamble to the final rule. 44 Fed.Reg. at 33587, col. 3. The new standards contested on this appeal went into effect immediately upon promulgation in June 1979 and remain in force pending the final resolution of the dispute. See 42 U.S.C. §§ 7411(b)(1)(B), 7411(a)(2).
     
      
      . 44 Fed.Reg. at 33587, col. 3.
     
      
      . Ad.Doc.No. V-C-2, supra note 10, at 3, J.A. at 3131; Ad.Doc.No. III-B-3, supra note 9, at 5-28, J.A. at 1966.
     
      
      . Ad.Doc.No. V-C-2, supra note 10, at 1, J.A. at 3129.
     
      
      . Id. See 44 Fed.Reg. at 33609, Table 5 (Figure 8 in the appendix to this opinion).
     
      
      . 44 Fed.Reg. at 33606, cols. 2-3.
     
      
      . Id. at 33587, col. 3.
     
      
      . “Fact Sheet Hand-out on Summary of Standards,” Distributed at Administrator Costle’s Press Conference on May 25, 1979, 10, J.A. 3133, 3142, 3152 (Ad.Doc.No. V-C-l). See also “Press Briefing by Administrator Costle Announcing Proposed Standards,” 6-7, J.A. 2941, 2947-48 (EPA Sept. 11, 1978 (Ad.Doc.No. III-C-1).
     
      
      . 44 Fed.Reg. at 33587, col. 3, and at 33609, Table 4 (Figure 7 in the appendix to this opinion). Coal production and consumption were expected to triple under any of the alternative standards considered by EPA.
     
      
      . Ackerman & Hassler, supra note 8, at 1468.
     
      
      . Id. (citing Coal-Bridge to the Future: Report of the World Coal Study 245 (C. Wilson ed. 1980)); Ad.Doc.No. III-B-3, supra note 9, at 5-2 to 5-3; J.A. at 1940-41.
      The World Coal Study predicts that coal will be the primary energy source for 55 percent to 57 percent of the electricity produced in the United States by the year 2000. Due to increased overall demand for electric power by the turn of the century, this increased market share may well generate an increase of 100 percent to 200 percent in the amount of coal burned to generate electricity. Id. But see Taylor, supra note 9.
      Citations to other studies on the future of the coal-burning power plant are collected in Ackerman & Hassler, supra note 8, at 1468 n.5.
      See also Council on Environmental Quality, Global Energy Futures and the Carbon Dioxide Problem (1981); United States Regulatory Council, Cooperation and Conflict: Regulating Coal Production (1981).
     
      
      . The briefs submitted to this court on the merits total over 670 pages, the Joint Appendix contains 5,620 pages in twelve volumes, and the certified index to the record lists over 2,520 submissions. By the time of the publication of the final rule (EPA’s statement accompanying the final rule took up 43 triple columns of single spaced type), EPA had performed or obtained from contractors approximately 120 studies, and collected over 400 items of reference literature, received almost 1,400 comments, written 650 letters and 200 interagency memos, held over 50 meetings and substantive telephone conversations with the public, and conducted four days of public hearings. The complexity of the subject matter is discussed in C. Schultze, The Public Use of Private Interest 9-10 (1977) (see quotation at n.526 infra ) and Del Duca, supra note 8.
     
      
      . Section 111 of the Clean Air Act, 42 U.S.C. § 1857c-6 (1970) (now codified as amended at 42 U.S.C. § 7411). Since 1967 the centerpiece of the Clean Air Act has been the provision for setting National Ambient Air Quality Standards (NAAQS). NAAQS define ambient concentrations of harmful substances at levels determined to be necessary to protect public health and welfare. NAAQS are enforced by the states through emission limitations set on a source-by-source basis at a level which ensures that the ambient concentrations defined by NAAQS are not exceeded. By 1970 there was concern that NAAQS would constrain economic growth by limiting the construction of new sources as ambient concentrations of a designated substance approached the NAAQS, and by imposing costly requirements for retrofitting additional control technology on existing sources in cases where ambient concentrations of a substance did increase to meet or exceed NAAQS. In addition, Congress was concerned that the NAAQS system of air quality regulation would place states with relatively cleaner air at an economic advantage, since these states could attract industry by setting less stringent emission limits. The Environmental Policy Division, Congressional Research Service, The Library of Congress, 93d Cong., 2d Sess., A Legislative History of the Clean Air Act Amendments of 1970, 227, 260, 384, 816, 838, 844, 893, 1366 (Comm.Print 1974). To remedy these problems created by the established system of health-based regulation, Congress amended the Clean Air Act in 1970 to require major new sources to meet performance standards reflecting the best system of adequately demonstrated emission reduction, cf. text at notes 82-83 infra (purposes and intended effect of NSPS reiterated in 1977 Amendments).
     
      
      . Section 111(b)(1)(A), 42 U.S.C. § 1857 c-6(b)(1)(A) (1970) (now 42 U.S.C. § 7411(b)(1)(A)).
     
      
      . 36 Fed.Reg. 5931 (Mar. 31, 1971).
     
      
      . 36 Fed.Reg. 24876 (Dec. 23, 1971).
     
      
      . Id.
      
     
      
      . Oljato Chapter of the Navajo Tribe v. Train, 515 F.2d 654, 656 (D.C.Cir.1975).
     
      
      . The Indian petitioners previously had filed an action in the District Court for the District of Columbia. The District Court dismissed, ruling that review was available only in the Court of Appeals for the District of Columbia Circuit. This court ruled that the record compiled below was insufficient to permit effective judicial review. The court instructed the Indian petitioners to file a formal petition with EPA, and admonished EPA that a serious, substantive response was required. Oljato Chapter of the Navajo Tribe v. Train, 515 F.2d 654, 667 (D.C.Cir.1975).
     
      
      . 42 Fed.Reg. 5121 (Jan. 27, 1977).
     
      
      . 42 U.S.C. 7411(b)(6).
     
      
      . 44 Fed.Reg. 33580 (June 11, 1979).
     
      
      . 45 Fed.Reg. 8210 (Feb. 6, 1980). In denying the petitions, EPA found that the petitioners had failed to satisfy the statutory requirements of section 307(d)(7)(B) of the Clean Air Act, 42 U.S.C. 7607(d)(7)(B). That is, the petitioners failed to demonstrate either (1) that it was impracticable to raise their objections during the period for public comment or (2) that the basis of their objection arose after the close of the period for public comment and the objection was of central relevance to the outcome of the rule. Id.
      
     
      
      . 44 Fed.Reg. at 33580, cols. 2-3.
     
      
      . Id.
      
     
      
      . Power plants burning coal with potential sulfur dioxide emissions greater than 2 lbs./MBtu but less than 6 lbs./MBtu have to reduce emissions by more than 70 percent but less than 90 percent in order to achieve the 0.60 lbs./MBtu floor. The percentage reduction requirement therefore varies from 70 percent to 90 percent as the sulfur content of the coal being burned varies from 2 Ibs./MBtu (or less) to 6 lbs./MBtu (or more). Brief for Respondent EPA at 18 & Appendix B (chart).
     
      
      . See discussion of scrubbing technology text at nn.69-80 infra.
      
     
      
      . There are several significant statutory questions which we do not decide in this case, because no party has raised them.
      First, we are not presented with the question whether the Act permits a standard that requires scrubbing by all utility plants. No party before the court argues that a standard which requires scrubbing in all cases for compliance is contrary to the Act. Rather, the focus of this litigation has been on the appropriate level of pollution control that EPA should require. Brief for Petitioner APCO at 59; Brief for Intervenor APCO at 4, 8 n.10, & 22. In fact, EPA and Sierra Club believe that the Act requires all coal firing utility plants to use scrubbers. Brief for Respondent EPA at 64-65; Brief for Petitioner Sierra Club at 32-38. See generally and compare Ackerman & Hassler, supra note 8.
      Second, as a corollary, it is not necessary for us to decide, and we do not hold, that section 111 of the Act imposes a universal scrubbing requirement or otherwise mandates some specific method for achieving compliance with NSPS. On the contrary, section 111(h) permits EPA to specify a “design, equipment, work practice, or operational standard” only if it is “not feasible” to allow sources of pollution to choose the control technology they will employ to meet emission standards. The definition of situations where it is “not feasible” to allow dischargers of pollution to choose their own control technology is extremely limited. 42 U.S.C. § 7411(h)(2). See also 42 U.S.C. § 7411(b)(5). As a practical matter if the percentage reduction requirement is sufficiently stringent, then scrubbing will be necessary at all emission sources in order to meet the NSPS, given the present state of technology. As noted, both EPA and Sierra Club adopt the view that the percentage reduction requirement must be set high enough to “require that all power plants use scrubbers,” e. g., Brief for Respondent EPA at 64-65; Brief for Petitioner Sierra Club at 32-38. But section 111 does not on its face mandate any particular percentage. The “standard of performance” defined in section 111(a) is required to “reflect the degree of emission limitation and the percentage reduction achievable through application of the best technological system of continuous emission reduction which .. . the Administrator determines has been adequately demonstrated.” 42 U.S.C. § 7411(a)(1). In turn, the term “technological system of continuous emission reduction” is defined to mean “a technological process for production or operation by any source which is inherently low-polluting or nonpolluting,” or “a technological system for continuous reduction of the pollution generated by a source before such pollution is emitted into the ambient air, including precombustion cleaning or treatment of fuels.” 42 U.S.C. § 7411(a)(7). This is not an explicit textual mandate to use scrubber technology. While there is no universal scrubbing requirement elsewhere on the face of the statute, the House Committee Report explains that by requiring a “technological system” section 111 requires the use of scrubbers or other “add-on” technology and not just the use of untreated low sulfur coal. H.R.Rep. No. 1175, 94th Cong., 2d Sess. 161, 129-30 (1976), reprinted in The Environmental Policy Division, Congressional Research Service, The Library of Congress, 95th Cong., 2d Sess. 7 A Legislative History of the Clean Air Act Amendments of 1977 [hereinafter L.H.] 6547, 6710. [After first full citation legislative materials will be cited if possible by their Legislative Document Number, e. g., “H.R.Rep.No--” with a reference back to the place in the opinion where the full citation occurs, followed by parallel citations to the original page numbers, and the prepared Legislative History “L.H.” Thus the above-cited reference would hereinafter appear as H.R.Rep.No. 1175, supra note 38, at 161, 7 L.H. at 6710.]; see also H.R.Rep. Conf.No.95-564, 95th Cong., 2d Sess. 129-30 (1977), U.S.Code Cong. & Admin.News 1077, 1502, 3 L.H. 381, 509-10 (Conference Report) (the Conference agreement was tailored “to preclude use of untreated low sulfur coal alone as a means of compliance”). But see Ackerman & Hassler, supra note 8, at 1494-511, 1560 (discussing legislative history of section 111 and its significance in interpreting the statute) and Currie, supra note 8, at 1425-31.
      Third, we do not decide whether the Act prohibits the use of low sulfur coal alone as a method of compliance. No party presently advocates NSPS which could be satisfied by burning untreated low sulfur coal alone, without utilizing scrubbers or other “add-on” control technology. Instead the parties share the view that the Act prohibits reliance on burning untreated low sulfur coal alone as a system of emission control. E. g., Brief for Petitioner Sierra Club at 34, 38; Brief for Respondent EPA at 64-65; Brief for Intervenor APCO at 12; this position adheres to the statements in the House Committee Report and the Conference Committee Report, H.R.Rep.No.94-1175, supra at 161, 7 L.H. at 6710; H.R.Rep.No.95-564, supra at 130, 3 L.H. 509-10. But see Ackerman & Hassler, supra at 1494-511 and Currie, supra at 1425-31.
     
      
      . No party on this appeal opposes the variable standard on the basis that the 70 percent floor is too strict and should be lowered. Brief for Intervenor APCO at 8 n.10 & 22. Although during the rulemaking there were advocates for minimum percentage reduction requirements lower than the 70 percent floor ultimately promulgated in the final NSPS, the only objection before the court to the 70 percent minimum level of sulfur dioxide reduction is Sierra Club’s challenge that it is too lax and should be increased.
      The Electric Utilities’ position is “we do not believe that the variable control option chosen by the Administrator represented the variable control alternative which reflects the best balance among the statutory criteria. However, under existing standards of judicial review in this Circuit, the Administrator’s detailed analysis of alternative standards and comments filed on those analyses are more than sufficient to negate a claim of ‘arbitrariness and irrationality’ in the formulation of the final 70 percent variable control rule.” Id. at 22 (footnote omitted). However, the Electric Utilities urge that if this court remands the variable standard for reconsideration, that EPA be instructed to reconsider lowering as well as raising the 70 percent floor. Id. at n.50.
     
      
      . Many of the procedural disputes involved in petitioner EDF’s challenge to the 1.2 lbs./MBtu emission ceiling do not appear to be “centrally relevant to the outcome” of the variable standard even though the emission ceiling and the variable standard are integral components of the overall NSPS and are, of course, closely related. While recognizing that the evolution and intended effects of each part of the NSPS cannot be analyzed completely independently, we find it less confusing to separately consider the procedural issues raised by Sierra Club directly related to variable control, and EDF’s procedural challenge which goes more directly to the propriety of the emission ceiling.
     
      
      . EPA’s construction of the Clean Air and Water Acts has been accorded considerable deference by the courts. EPA v. National Crushed Stone Ass’n, 449 U.S. 64, 83-85, 101 S.Ct. 295, 306-307, 66 L.Ed.2d 268 (1980); Lead Industries Ass’n v. EPA, 647 F.2d 1130 at 1147-1148, (D.C.Cir.1980), cert. denied, 449 U.S. 1042, 101 S.Ct. 621, 66 L.Ed.2d 503 (citing Union Electric Co. v. EPA, 427 U.S. 246, 256, 96 S.Ct. 2518, 2525, 49 L.Ed.2d 474 (1976); Train v. Natural Resources Defense Council, Inc., 421 U.S. 60, 75, 95 S.Ct. 1470, 1479, 43 L.Ed.2d 731 (1975); Ethyl Corp. v. EPA, 541 F.2d 1, 12 n.16 (D.C.Cir.) (en banc), cert. denied, 426 U.S. 941, 96 S.Ct. 2662, 49 L.Ed.2d 394 (1976)).
     
      
      . Consumer Product Safety Commission v. GTE Sylvania, 447 U.S. 102, 108, 100 S.Ct. 2051, 2056, 64 L.Ed.2d 766 (1980); Ernst & Ernst v. Hochfelder, 425 U.S. 185, 197, 96 S.Ct. 1375, 1382, 47 L.Ed.2d 668 (1976).
     
      
      . 42 U.S.C. § 741 l(a)(l)(A)(ii).
     
      
      . 42 U.S.C. § 7411(b)(2).
     
      
      . Cf., Asarco, Inc. v. EPA, 578 F.2d 319, 330-31 (D.C.Cir.1978) (Leventhal, J., concurring). In Asarco, Judge Leventhal noted EPA’s flexibility under section 111(b)(2) (formerly codified in identical form at 42 U.S.C. § 1857c-6(b)(2)) to distinguish between newly constructed and modified smelting facilities within the larger industrial category of smelting facilities. See also Ackerman & Hassler, supra note 8, at 1509; Currie, supra note 8, at 1428-31.
     
      
      . 42 U.S.C. § 7411(a).
     
      
      . The House Report had stated that “[i]n the case of fuel-burning new stationary sources, the standard must require a specified percentage reduction in emissions achievable when applying best technology to untreated fuels.” But no percentage reduction requirement was included in the text of the House bill. H.R.Rep. No.95 — 294, 95th Cong., 1st Sess. 188 (1977), 4 L.H. at 2655. The Senate bill contained no amendments to this part of section 111.
     
      
      . H.R.Conf.Rep.No.564, supra note 38, at 130, 3 L.H. at 510.
     
      
      . Clean Air Act Conference Report: Statement of Intent; Clarification of Select Provisions, 123 Cong.Rec. 27071 (1977), 3 L.H. at 324.
     
      
      . 123 Cong.Rec. 26846 (1977), 3 L.H. at 353 (remarks of Sen. Muskie). Senator Muskie’s statement that “standards with a degree of uniformity are needed” also recognizes, by implication, that some degree of variation is tolerable, and that rigid adherence to uniformity is not needed.
     
      
      . Brief for Petitioner Sierra Club at 38.
     
      
      . “Any such range of percent reduction would be allowed only to reflect varying fuel characteristics.....” 123 Cong.Rec. 27071 (1977), 3 L.H. at 324 (statement submitted by Rep. Rogers).
     
      
      . See n.49 supra and accompanying text.
     
      
      . 123 Cong.Rec. 18515 (1977), 3 L.H. at 1146 (quoted by Brief for Petitioner Sierra Club at 39).
     
      
      . We note that “[t]he remarks of a single legislator, even the sponsor, are not controlling in analyzing legislative history.” Chrysler 
        
        Corp. v. Brown, 441 U.S. 281, 311, 99 S.Ct. 1705, 1722, 60 L.Ed.2d 208 (1979). In this instance, Senator Domenici’s statement was offered in opposition to the imposition of any percentage reduction requirement at all, and in fact, he opposed the 1977 Amendments to the Act. Accordingly, Senator Domenici’s interpretation of the House bill is not determinative of the meaning of the Act. Holtzman v. Schlesinger, 414 U.S. 1304, 1312 n.13, 94 S.Ct. 1, 6 n.13, 38 L.Ed.2d 18 (1973); see also NLRB v. Fruit & Vegetable Packers & Warehousemen Local 760, 377 U.S. 58, 66, 84 S.Ct. 1063, 1068, 12 L.Ed.2d 129 (1964); American Airlines, Inc. v. CAB, 365 F.2d 939, 949 (D.C.Cir.1966).
     
      
      . The Conference Committee Report states that the NSPS should “preclude use of untreated low sulfur coal alone as a means of compliance.” H.R.Rep.No.95-564, supra note 38, at 130, 3 L.H. at 510. This statement certainly does not amount to an explicit prohibition against considering the sulfur content of coal when promulgating the percentage reduction requirement, and we are not persuaded that the statement can be read as an indirect admonition against variable control. See Brief for Petitioner Sierra Club at 38 (citing H.R.Rep.No. 95-564, supra). No utility plant can achieve the variable 70 to 90 percent standard actually adopted simply by burning low sulfur coal. Scrubbing alone or some combination of add-on technology must necessarily be employed.
      Sierra Club argues to the contrary, that variable control would permit burning low sulfur coal alone because utilities would be able to by-pass part of their waste stream around the scrubber and still comply with the standard. Brief for Petitioner Sierra Club at 38 (quoting 44 Fed.Reg. at 33583, col. 1).
      We note, initially, that by-passed flue gas can be considered untreated only if no other add-on technology like coal washing is employed and a substantial percentage of coal can be expected to be pretreated under the new standard. See text at nn. 288-310 infra. But in any case the flue gas by-pass argument seems to us beside the point. Utilities are only required to achieve overall emission and percentage reductions in accordance with the NSPS. The Act does not address the question of how much of the waste stream has to be scrubbed — it does not even explicitly mandate scrubbing. Instead, the Act instructs EPA to set a percentage reduction requirement which reflects a variety of criteria without foreclosing a degree of flexibility in approaches to achieving the standard.
     
      
      . Conference Committee Statement of Intent, supra note 49; remarks of Sen. Muskie, supra note 50.
     
      
      . Id.
      
     
      
      . See text at nn. 138-54 infra.
      
     
      
      . The lengthy debates that preceded the passage of the 1977 Amendments reflected concern that the standards be flexible and that EPA have broad discretion to account for varying circumstances. For example, during the debate on the Senate bill (S. 252) Senate spokesmen emphasized on several occasions their desire not to follow the House bill (H. 6161) if it were to be interpreted as requiring “EPA to compel the use of scrubbers at all new coal-fired powerplants in the United States.” Remarks of Senator Bumpers, 123 Cong.Rec. 18168 (1977), 3 L.H. at 958; remarks of Senator Baker, 123 Cong.Rec. 18489-90 (1977), 3 L.H. at 1094-95. Senator Muskie assured the Senators that the Act was not so rigid. Remarks of Senator Muskie, 123 Cong.Rec. 18168 (1977), 3 L.H. at 958. And Senator Garn believed that low sulfur coal or “clean coal” should be treated differently by the standards. 123 Cong.Rec. 18043-44 (1977), 3 L.H. at 782-83.
     
      
      . Brief for Petitioner Sierra Club at 39-42 (citing Chemehuevi Tribe of Indians v. FPC, 420 U.S. 395, 403, 95 S.Ct. 1066, 1072, 43 L.Ed.2d 279 (1975) (all parts of a statute must be read together)).
     
      
      . Part C — Prevention of Significant Deterioration of Air Quality, sections 160-69, 42 U.S.C. §§ 7470-79; Part D — Plan Requirements for Nonattainment Areas, sections 173(2), 42 U.S.C. §§ 7503(2), 7501(3).
     
      
      . I. e., section 169A, 42 U.S.C. § 7491.
     
      
      . See text at nn. 104-65 infra. Sierra Club also disagrees with EPA’s finding that variable control does not undermine the essential purposes of the Act. This dispute presents a question of record analysis and the parties agree on the relevant statutory purposes, i. e., those defined in the Conference Committee Report, H.R.No.95-564, supra note 38, at 130, 3 L.H. at 510. But see Ackerman & Hassler, supra note 8, at 1510.
     
      
      . 44 Fed.Reg. at 33584, col. 1. E. g., states may impose more stringent limitations on emissions under sections 110 and 116, 42 U.S.C. §§ 7410, 7416. New sources also may be subject to restrictions: to prevent significant deterioration of air quality, under sections 165(a), 169(1) and 169(3), 42 U.S.C. §§ 7475(a), 7479(1), 7479(3); to improve air quality in nonattainment areas under section 173, 42 U.S.C. § 7503; and to protect visibility under sections 165(d), 169A, 42 U.S.C. §§ 7475(d), 7491.
     
      
      . Lead Industries Ass’n v. EPA, 647 F.2d 1130 at 1147 (D.C.Cir.1980), cert. denied, — U.S. —, 101 S.Ct. 621, 66 L.Ed.2d 268 (quoting Automotive Parts & Accessories Ass’n v. Boyd, 407 F.2d 330, 336, 338 (D.C.Cir.1968)); National Lime Ass’n v. EPA, 627 F.2d 416, 429-30 (D.C.Cir.1980).
     
      
      . 42 U.S.C. § 7607. If the agency’s decision is not based on substantial evidence then it will be held to be arbitrary and capricious. Lead Industries Ass’n v. EPA, supra at 26 n.29.
     
      
      . Essex Chemical Co. v. Ruckelshaus, 486 F.2d 427, 434 (D.C.Cir.1973); Portland Cement Ass’n v. Ruckelshaus, 486 F.2d 375 (D.C.Cir.1973), cert. denied, 417 U.S. 921, 94 S.Ct. 2628, 41 L.Ed.2d 226 (1974); Home Box Office, Inc. v. FCC, 567 F.2d 9, 35 (D.C.Cir.), cert. denied, 434 U.S. 829, 98 S.Ct. 111, 54 L.Ed.2d 89 (1977).
     
      
      . The range of principal FGD processes is considerably broader and the distinctions between different types are more numerous than is suggested by the single wet scrubber-dry scrubber dichotomy which the parties have focused on. Cf. Brief for Respondent EPA at 34-36. For example, one major distinction is between throwaway processes, in which all waste streams are discarded, and regenerable processes in which the sorbent is regenerated and recycled. In certain regenerable processes, elemental sulfur or sulfur compounds can be recovered from waste streams as marketable products.
      Flue gases can be treated through wet, semi-dry, or dry desulfurization processes of both throwaway and recovery types. Wet FGD processes are subdivided further into the categories of slurry processes and clear liquor processes. In slurry processes a suspension of active sorbent is used to contact or scrub the gas stream. Examples of slurry processes are lime and limestone scrubbing (see text infra) and the regenerable magnesium oxide (MA-GOX) process. Clear liquor desulfurization processes involve various scrubbing solutions including sodium carbonate (used in the throwaway, “single alkali” process), sodium sulfite (“double-alkali” process and “Wellman-Lord” process), and ammonia.
      In the semidry FGD process, small quantities of spray containing sodium carbonate contact the flue gas. The spent sorbent is either discarded or regenerated. Dry throwaway FGD processes entail, for example, the use of nahcolite (a mineral containing natural sodium bicarbonate) or limestone (consisting mainly of calcium carbonate) injected into the boiler. Two dry regenerable FGD processes are the carbon adsorption and copper oxide processes.
      There are advantages and disadvantages to these and other variations of FGD in the context of any particular industrial situation.
      
        See “Overview of Flue Gas Desulfurization Processes,” Ad.Doc. No. III-B-3, supra note 9, at 4-60 to 4-64, J.A. at 1846-50.
      
        See also “Flue Gas Desulfurization Systems,” Flue Gas Desulfurization System Capabilities for Coal-Fired Steam Generators, Vol. II, Technical Report, at 3-1 to 3-357, J.A. 477, 515-871 (EPA Pub.No.600/ 7-78-032b, March 1978) (Ad.Doc. No. II — A — 71).
     
      
      . In addition to FGD, methods for limiting emissions of sulfur compounds fall into three broad categories: (1) burning low sulfur coal, (2) cleaning coal before combustion to remove part of the sulfur content, and (3) retaining sulfur during or immediately following combustion in sorbent material mixed with fuel coal (e. g., fluidized bed combustion). These techniques may also be used in combination with FGD to achieve a given degree of sulfur retention. Ad.Doc.No. III-B-3, supra note 9, at 4-l to 4-60, J.A. at 1787-1846.
     
      
      . Id. at 4-60 to 4-130, J.A. at 1846-1916; Ad.Doc. No. II-A-71, supra note 69, at 3-2 to 3-8, J.A. at 515-22; Ackerman & Hassler, supra note 8, at note 56.
     
      
      . Id.
      
     
      
      . “The final S02 standards are based on the performance of a properly designed, installed, operated and maintained FGD system. Although the standards are based on lime and limestone FGD systems, other commercially available FGD systems (e. g., Wellman-Lord, double alkali and magnesium oxide) are also capable of achieving the final standard.” 44 Fed.Reg. at 33592, col. 1.
     
      
      . Ad.Doc. No. III-B-3, supra note 9, at 4-76 to 4-95, J.A. at 1862-81.
     
      
      . Wet scrubbers have been in commercial use in the United States since the late 1960’s and early 1970’s. 37 Fed.Reg. 5768-69 (1972). See generally “History of FGD Systems,” Ad.Doc. No. II-A-71, supra note 69, at 1-1 to 1-3, J.A. at 493-95. Since that time the use of wet scrubbing has increased substantially while the performance of the systems has improved significantly. Ad.Doc. No. II-A-71, supra, at 4-1 to 4-38, J.A. at 873-910.
      During the late 1970’s dry scrubbing control systems emerged as potential alternatives to wet scrubbing. “Dry S02 Control,” Electrical Utility Steam Generating Units: Background Information for Promulgated Emission Standards, 3-60 to 3-76, J.A. 2359, 2664-80 (EPA Pub.No.450/3-79-021, June 1979) (Ad.Doc. No. V-B-l). At the time EPA issued the NSPS three full scale dry scrubbing systems were being installed on utility boilers and were scheduled to start operation in 1981-82. Bids were sought for five more dry control systems for “utility applications.” 44 Fed.Reg. at 33582, col. 3.
     
      
      . Activity in the dry S02 control field is being stimulated by several factors. First, dry control systems are less complex than wet technology. These simplified designs offer the prospect of greater reliability at substantially lower costs than their wet counterparts. Second, dry systems use less water than wet scrubbers, which is an important consideration [at least] in the Western part of the United States. Third, the amount of energy required to operate dry systems is less than that required for wet systems. Finally, the resulting waste product is more easily disposed of than wet sludge.
      44 Fed.Reg. 33582, col. 2; Ad.Doc. No. III-B-3, supra note 9, at 4 — 63, J.A. at 1849; Ad.Doc. No. V-B-l, supra at 3-66 to 3-75, J.A. at 2670-79.
     
      
      . 43 Fed.Reg. 42160, col. 1.
     
      
      . Wet scrubbing may also involve multiple stages. For example, while wet scrubbing can remove both fly ash and sulfur dioxide simultaneously from a gas stream it may be desirable to collect fly ash separately by means of a baghouse or electrostatic precipitator. Possible interference with the process reactions is avoided by removing the fly ash upstream of the desulfurizing unit, and erosion of the desulfurization process equipment is reduced. The volume of sludge is also minimized when the fly ash is removed prior to the desulfurization process. In addition, contamination of the reagents and by-products is prevented. Ad. Doc. No. III-B-3, supra note 9, at 4-62, J.A. at 1848.
     
      
      . Ad.Doc. No. V-B-l, supra note 75, at 3-60, J.A. at 2664.
      “A11 wet processes cause a considerable cooling of the treated flue gas and an increase in its moisture content. Reheat of the gas prior to discharge may be desirable in certain applications to avoid condensation and corrosion in ducts, fans and stacks downstream of the scrubber and to restore the buoyancy of the flue gas entering the stack. These drawbacks are largely circumvented in semidry and dry processes. Further, the disposal of solid wastes generated in semidry and dry throwaway processes may be easier than the disposal of sludges and liquid wastes.” Ad.Doc. No. III-B-3, supra note 9, at 4-63, J.A. at 1849.
     
      
      . Id.
      
     
      
      . 42 U.S.C. § 7411(a)(1).
     
      
      . See text at nn.49 & 50 supra.
      
     
      
      . 44 Fed.Reg. at 33581, col. 3-33582, col. 1. (EPA summarizing the six purposes identified in H.R.Rep.No.95-294, supra note 47, at 184-86, 4 L.H. at 2651-53.)
     
      
      . E. g., Reply Brief for Petitioner Sierra Club at 13.
     
      
      . See text at n.81 supra, Brief for Petitioner Sierra Club at 35-36.
     
      
      . Essex Chemical Corp. v. Ruckelshaus, 486 F.2d 427, 438-39 (D.C.Cir.1973); Portland Cement Ass’n v. Ruckelshaus, 486 F.2d 375, 386 n.42 (D.C.Cir.1973); see also Ackerman & Hassler, supra note 8, at 1479-80; Currie, supra note 8, at 1420-25.
     
      
      . 43 Fed.Reg. at 42154, col. 2, 42155, col. 2.
     
      
      . Id. at 42158, col. 3. The five wet scrubbing methods found to be adequately demonstrated for 85 percent removal efficiency were the lime, limestone, Wellman-Lord, magnesium oxide, and double-alkali techniques.
     
      
      . Id. at 42155, col. 1. See also Ad.Doc.No. III-C-1, supra note 18, at 14-15, J.A. at 2955-56.
     
      
      . See 43 Fed.Reg. at 42159, col. 3, 42161, col. 3.
     
      
      . See 44 Fed.Reg. at 33603, col. 1-33604, col. 3. The key modeling assumptions are stated in Table 1, id. at 33608, cols. 1-2 (shown as Figure 4 in the appendix to this opinion). See also 43 Fed.Reg. 57834 (Dec. 8, 1978).
     
      
      . See the description of the new alternatives analyzed in 43 Fed.Reg. at 57835, cols. 1-3.
     
      
      . Id. at 57834-36.
     
      
      . “Transcript of Proceedings of Public Hearing,” J.A. 2965 (Dec. 12-13, 1978) (Ad.Doc.No. IV-F-1).
     
      
      . Phase 3 also included analysis — separate from the econometric modeling — of regional coal production impacts. This analysis related to the 1.2 lbs./MBtu standard discussed in a later section of this opinion.
     
      
      . 44 Fed.Reg. at 33605, col. 3.
     
      
      . Id. at 33605, col. 3-33609, col. 3.
     
      
      . Id.
      
     
      
      . 44 Fed.Reg. at 33580 (June 11, 1979).
     
      
      . Id. at 33597, col. 1.
     
      
      . Id. at 33597, col. 2.
     
      
      . See text at nn. 138-39, 162 infra.
      
     
      
      . id. at 33583, col. 3—33584, col. 1.
     
      
      . Reply Brief for Petitioner Sierra Club at 14. Sierra Club’s grievance with EPA’s modeling approach is closely related to its interpretation of section 111 which we have rejected. See text at nn.41-65 supra.
      
     
      
      . Our conclusion that national air emissions are a relevant factor to be considered in picking a “best technological system” precludes Sierra Club’s argument that Congress meant, by excluding air emissions as a factor for EPA to balance under section 111, to-foreclose the kind of “speculation” in which EPA necessarily involved itself here in projecting future air emissions — e. g., its controversial predictions about how utilities would behave under alternative standards.
     
      
      . 42 U.S.C. § 7411(a)(1).
     
      
      . In nonattainment areas, the permit requirements for new or modified major stationary sources are specified by 42 U.S.C. § 7503 which provides inter alia that “the proposed source is required to comply with the lowest achievable emission rate," 42 U.S.C. § 7503(2) (emphasis supplied), defined as:
      (A) the most stringent emission limitation which is contained in the implementation plan of any State for such class or category of source, .... or
      (B) the most stringent emission limitation which is achieved in practice by such class or category of source, whichever is more stringent.
      42 U.S.C. § 7501(3).
      The Conference Committee Report explained:
      In determining whether an emission rate is achievable, cost will have to be taken into account, but cost factors in the nonattainment context will have somewhat less weight than in determining new source performance standards under [section 111].
      H.R.Rep.No.564, supra note 38, at 157, U.S. Code Cong. & Admin.News at 1538, 3 L.H. at 537. See also Remarks of Senator Muskie introducing S. 252 for debate, 123 Cong.Rec. 18018 (1977), 3 L.H. at 717 (indicating broad discretion allowed EPA under section 111 “is inappropriate” in nonattainment areas “where public health is at risk”).
     
      
      . Rather, the amendments to section 111 made explicit the broad discretion that was implicit in the previous language. H.R.Rep.No. 294, supra note 47, at 190, 4 L.H. at 2657, citing Essex Chemical and Portland Cement, see nn.109 & 110, infra; see also Remarks of Senator Muskie, supra note 107, and Currie, supra note 8, at 1421.
     
      
      . 486 F.2d 427, 431 (D.C.Cir.1973).
     
      
      . 486 F.2d 375, 384-85 (D.C.Cir.1973), cert. denied, 417 U.S. 921, 94 S.Ct. 2628, 41 L.Ed.2d 226 (1974).
     
      
      . Id. at 384.
     
      
      . Id. at n.42.
     
      
      . Conference Committee Statement of Intent, supra note 49 (referring to H.R.Rep.No. 95-294, supra note 47, at 183-95, 4 L.H. at 2651-62, Remarks of Sen. Muskie, supra note 107.
     
      
      . See generally S.Rep.No.95-127, 95th Cong., 1st Sess. (1977), 3 L.H. 1371; H.Rep.No.95-294, supra note 47, 4 L.H. 2465.
     
      
      . 44 Fed.Reg. at 33605, col. 1. See Del Duca, The Clean Air Act: A Realistic Assessment of Cost Effectiveness, 5 Harv.Env.L.Rev. 184, 192-96 (1981).
     
      
      . EPA’s Administrator stated:
      The truth of the matter is that the model that we are using is a reasonably good model, but you can alter the outcome from that model dramatically by just simply changing a few key initial assumptions that you crank into the model. I think those assumptions need to be tested, frankly, in a public debate and in a formal rulemaking proceeding, where people comment for the record, set out their alternative assumptions, saying, “We think this is really more realistic.”
      Ad.Doc. No. III-C-1, supra note 18, at 15-16, J.A. at 2956-57.
     
      
      . Id. at 7, 15-16, J.A. at 2948, 2954-55. Although the model “produces precise numbers, it is not a precise model because of the uncertainties and inaccuracies of its assumptions. Its chief value is the aid it provides to organized thinking about important policy variables and the qualitative relations between them.” Del Duca, supra note 115, at 195.
     
      
      . For example, the task of anticipating trends in oil prices is obviously fraught with difficulty. Or, as the Administrator pointed out:
      Those models are terribly sensitive to the assumptions that you make. For example, they assume that, when utility managers must manage these investments and make a decision, they choose the most economically efficient alternative. This is a modeling assumption; it may not be true in real life.
      Ad.Doc. No. III-C-1, supra note 18, at 7, J.A. at 2948.
     
      
      . E. g., Reply Brief for Petitioner Sierra Club at 14-15; Brief for Petitioner Sierra Club at 2, 14-15.
     
      
      . 42 U.S.C. § 7617 requires EPA to perform an Economic Impact Assessment for, inter alia, the promulgation or revision of NSPS. Section 7617(c) requires EPA to assess:
      (1) the costs of compliance with any such standard or regulation, including extent to which the costs of compliance will vary depending on (A) the effective date of the standard or regulation, and (B) the development of less expensive, more efficient means or methods of compliance with the standard or regulation;
      (2) the potential inflationary or recessionary effects of the standard or regulation;
      (3) the effects on competition of the standard or regulation with respect to small business;
      (4) the effects of the standard or regulation on consumer costs; and
      (5) the effects of the standard or regulation on energy use.
      Nothing in this section shall be construed to provide that the analysis of the factors specified in this subsection affects or alters the factors which the Administrator is required to consider in taking any action referred to in subsection (a) of this section.
      42 U.S.C. § 7617(d) states that this assessment shall be “as extensive as practicable.” See also Exec. Order No. 12044, 3 C.F.R. 152-56 (March 24, 1978).
     
      
      . 567 F.2d 1016 (D.C.Cir.1977).
     
      
      . Id. at 1037.
     
      
      . Id. at 1039.
     
      
      . Ethyl Corp. v. EPA, 541 F.2d 1, 36 (D.C.Cir.) (en banc), cert. denied, 426 U.S. 941, 96 S.Ct. 2662, 49 L.Ed.2d 394 (1976); Amoco Oil Co. v. EPA, 501 F.2d 722, 740-41 (D.C.Cir.1974). See DeLong, Informal Rulemaking and the Integration of Law and Policy, 65 Va.L.Rev. 257, 285-86, 289, 294-95, 334-35, 341, 347 (1970). See also Aqua Slide 'N' Dive v. Consumer Product Safety Comm’n, 569 F.2d 831, 838 (5th Cir. 1978): “[T]he inability of any court to weigh diverse technical data also demands an inquiry to determine whether the Commission ‘carried out [its] essentially legislative task in a manner reasonable under the state of the record before [it].’ ”; United States v. Nova Scotia Food Products, 568 F.2d 240, 251 (2d Cir. 1977): “Though a reviewing court will not match submission against counter-submission to decide whether the agency was correct in its conclusion on scientific matters . .. it will consider whether the agency has taken account of all relevant factors and whether there has been a clear error of judgment.”
     
      
      . 43 Fed.Reg. at 42161, col. 2-42161, col. 3; Background Information for Proposed SO2 Standards: Supplement 2-1 to 3-26, J.A. 2251, 2263-307 (EPA Pub. No. 450/2-70-007a-l August 1978) (Ad. Doc. No. III-B-4). See also EPA’s discussion of the model at 43 Fed.Reg. at 57834, col. 2-57836, col. 2; 44 Fed.Reg. at 33602, col. 3-33607, col. 3; 45 Fed.Reg. at 8216, col. 2-8221, col. 2.
     
      
      . 44 Fed.Reg. at 33602, col. 3-33607, col. 3.
     
      
      . See, e. g., the Administrator’s comments quoted at nn.116, 118, supra.
      
     
      
      . See n.125 supra.
      
     
      
      . See, e. g., Portland Cement Ass'n v. Ruckelshaus, 486 F.2d 375, 393-94, 402 (D.C.Cir.1973), cert. denied, 417 U.S. 921, 94 S.Ct. 2628, 41 L.Ed.2d 226 (1974); Mobil Oil Corp. v. FPC, 483 F.2d 1238 (D.C.Cir.1973); Int’l Harvester Co. v. Ruckelshaus, 478 F.2d 615, 631-32 (D.C.Cir.1973). See also Aqua Slide ’N’ Dive Corp. v. Consumer Product Safety Comm’n, 569 F.2d 831, 838 (5th Cir. 1978); United States v. Nova Scotia Food Products Corp., 568 F.2d 240, 252 (2d Cir. 1977); DeLong, supra note 124, at 269, 273, 293. See Rodgers, Benefits, Costs, and Risks: Oversight of Health and Environmental Decisionmaking, 4 Harv.Env.L.Rev. 191, 214-18 (1980).
     
      
      . [T]he precise purpose of a statute may be to grant an agency responsibility for deciding questions characterized by a high degree of uncertainty.
      DeLong, supra note 124, at 289.
      Rulemaking invokes an amalgam of beliefs about the present facts; explicit or implicit theories about the way an industry, the economy, or the society works; predictions about the future development with and without a rule; analyses and guesses about costs and benefits as they will affect different groups; identification and assessment of risks and uncertainties; value judgments, and political calculations about the acceptability of regulation. The number of facts possibly relevant to some or all of the considerations is infinite. In some cases factual elements will predominate. In others the major issues may require the construction of predictive models about the effect of a rule. In still others, the question may concern the appropriate weighing of the risks involved.
      
        Id. at 294.
      The crucial questions are how to narrow the uncertainty and decide the proper course under conditions of uncertainty, given the consequences of error.... The issue for the court is whether the agency structured its decision to highlight uncertainty problems and deal with them rationally.
      
        Id. at 346-47 (footnotes omitted). See Rodgers, supra note 129, at 219-25.
     
      
      . These economic models are robed in the elegance of high-speed computers, but they are at base extrapolations from past experience, projections that must undergo continual examination and revision. They do not always have the reassuring concreteness of empirical observations, but they are the best we have to work with in casting our program's. Provided that the assumptions on which a model is based are adequately explained and justified, we see no reason why this type of evidence may not be used... .
      
        American Public Gas Ass’n v. FPC, 567 F.2d 1016, 1037 (D.C.Cir. 1977), cert. denied, 435 U.S. 907, 98 S.Ct. 1456, 55 L.Ed.2d 499 (1978). See also DeLong, supra note 124, at 319-38; Del Duca, supra note 115, at 195.
     
      
      . Pillai v. CAB, 485 F.2d 1018, 1027 (D.C.Cir. 1973) (artificial narrowing of options to one alternative found to be arbitrary and capricious); see American Public Gas Ass’n v. FPC, 567 F.2d 1016, 1037 (D.C.Cir. 1977); DeLong, supra note 124, at 338. DeLong describes the need for the structured use of information like the computer modeling employed in this case:
      [F]ew [policy] choices are easily bounded. Most have side effects, and in many cases these impacts, good or bad, outweigh the importance of the objective. Most government choices involve “polycentric problems” in which it is impossible to affect just one variable in a complicated web of interconnecting relationships. Because the government cannot restrict its effects to one area, analysis of these side effects is extremely difficult, and often impossible, especially when second, third or n th order consequences are involved.
      DeLong, supra at 329 & n.342 (citations omitted). DeLong continues:
      The basic policy analysis criticism of government is that agencies frequently do not structure decisionmaking processes in ways that make explicit the agency’s choices and the tradeoffs inherent in those choices. Consequently the agency may ignore or not collect important information, neglect technical analyses of the action’s impact, fail to consider regulatory costs or redistributive effects and generally avoid facing the complexity and the uncertain effects of the regulation, the relationship, or lack of one, between available resources and decided ends may be obscured, and possible alternative ways of achieving ends often will not be considered.
      
        Id. at 330.
     
      
      . See text at nn.139-42 infra.
      
     
      
      . 44 Fed.Reg. at 33607, col. 2.
     
      
      . EPA explained:
      The utility model selected for this analysis can be characterized as a cost minimizing economic model. In meeting demand it determines the most economic mix of plant capacity and electric generation for the utility system, based on a consideration of construction and operating costs for new plants and variable costs for existing plants. It also determines the optimum operating level for new and existing plants. This economic-based decision criteria should be kept in mind when analyzing the model results. These criteria imply, for example, that all utilities base decisions on lowest costs and that neutral risk is associated with alternative choices.
      
        Id. at 33603, col. 2-3.
     
      
      . The assumption of risk neutrality implies that a utility will always choose the low-cost option. However, EPA recognized that risk neutrality might not represent the utility decisionmaking process in all cases. Id. at col. 3.
     
      
      . We note support in the literature for the reasonableness of the finding that variable control would yield lower emissions than full control. Ackerman & Hassler, supra note 8, at 1524, 1539 n.301, 1543-44; Harrison & Portney, supra note 8, at 27.
     
      
      . The question of whether variable control is the best of all possible standards is not before the court. Sierra Club’s appeal only challenges the reasonableness of EPA’s finding that variable control is better than full control. See n.39 supra.
      
     
      
      . Reply Brief for Petitioner Sierra Club at 13 (citing 45 Fed.Reg. at 8219, Table 3). Sierra Club also asserted this contention during rebuttal at oral argument.
     
      
      . See 45 Fed.Reg. at 8218, col. 1-8220, col. 2.
     
      
      . Id. at 8220, col. 1.
     
      
      . Id. at cols. 1-2.
     
      
      . See nn. 62-63 supra.
      
     
      
      . Air quality and visibility are affected not solely by the amount of sulfur dioxide spewed into the air, but also by a host of other factors — e. g., the height of the stack, wind direction, the plant’s proximity to population centers and other meteorological and geographical factors. In addition, the literature suggests that sulfur dioxide is an inadequate measure of pollution problems. It may be, for example, that creation of sulfates (S04) compounds is a far more significant indicator of pollution problems than sulfur dioxide emissions. Ackerman & Hassler, supra note 8, at 1478-79; 1515-20. See also Report of the National Commission on Air Quality, supra note 8, at 3.9-1 to 3.9-33; Lee, Interstate Pollution: Proposed Amendments to the Clean Air Act, 5 Harv.Env.L.Rev. 71 (1981).
     
      
      . See 44 Fed.Reg. at 33607, col. 3, 33608 (Table 3) (Figure 6 in the appendix to this opinion).
     
      
      . Id.
      
     
      
      . Brief for Respondent EPA at 70; 44 Fed. Reg. at 33608-33609 (Tables 3-5) (Figures 6-8 in the appendix to this opinion).
     
      
      . 44 Fed.Reg. at 33584, col. 1.
     
      
      . H.R.Rep.No.95-564, supra note 38, at 130, 3 L.H. at 510.
     
      
      . 44 Fed.Reg. at 33583, col. 3.
     
      
      . 44 Fed.Reg. at 33609, Table 4 (Figure 7 in the appendix to this opinion).
     
      
      . Brief for Petitioner Sierra Club at 42 (quoting 44 Fed.Reg. at 33603, col. 3).
     
      
      . 44 Fed.Reg. at 33583, col. 3.
     
      
      . Members of the Missouri Association of Municipal utilities have weighed these important factors and have expressed a desire to continue use of medium sulfur Missouri coal. The variable control standard adopted by the Administrator makes the use of coal mined in this region economically attractive. Although the coal used by MAMU will have to be ‘scrubbed’ to reduce more than 70% of the sulfur dioxide emissions, it will not be subject to full scrubbing and the significantly higher costs associated with the extremely complex technology required for full scrubbing.
      Brief for Intervenor MAMU at 9.
     
      
      . 44 Fed.Reg. at 33582, col. 3-33583, col. 1. See n. 165 infra.
      
     
      
      . 44 Fed.Reg. at 33583, col. 3.
     
      
      . 43 Fed.Reg. at 42157, col. 3, 42158, cols. 2-3, 42160, cols. 1-2.
      Throughout the rulemaking EPA described dry scrubbing as an innovative or emerging technology. Nevertheless, at times EPA’s discussion comes close to suggesting that dry scrubbing may be adequately demonstrated. E. g. Brief for Respondent EPA at 63; see also 45 Fed.Reg. at 8217, cols. 1-2.
      Although it is conceivable that a particular control technique could be considered both an emerging technology and an adequately demonstrated technology, there is inherent tension between the two concepts, see e. g., Portland Cement Ass’n v. Ruckelshaus, 486 F.2d 375, 391-92 (D.C.Cir.1973); Int’l Harvester Co. v. Ruckelshaus, 478 F.2d 615, 628-29 (D.C.Cir.1973); Currie, supra note 8, at 1412-17.
      We feel compelled to state, so that there is no suggestion that the standard has been relaxed, that we do not hold that dry scrubbing is adequately demonstrated technology. Indeed, the record in this case would indicate the contrary.
      A report prepared for EPA as recently as February 1980 by a private contractor concludes;
      In summary, dry systems do offer potential advantages over wet systems, especially in the areas of energy savings and costs. However, crucial issues such as waste disposal and demonstration of commercial-scale systems, which may continue to limit the overall acceptability of this technology, remain to be answered.
      
      (Emphasis supplied.) “Survey of Dry SO2 Systems” 16-18 (EPA Pub.No. 600/7-80-030 Feb. 1980) included in part as Exhibit B in Brief for Petitioner Sierra Club.
      Previously EPA conceded that “no full scale dry scrubbers are presently in operation at utility plants so information available . . . dealt with prototype units.” 44 Fed.Reg. at 33594, col. 3. See also Ad.Doc. No. V-B-l, supra note 75, at 3-62, J.A. at 2666. EPA reported test results for dry scrubbers at the time the final rule was published. 44 Fed.Reg. at 33594, col. 3. See also results of pilot scale testing reported in the final background document, Ad.Doc. No. V-B-l, supra at 3-62 to 3-66, J.A. at 2666-2670. EPA does not attempt to explain how these results may be used to predict performance in full scale plants throughout the industry. The data standing alone is insufficient to establish that dry scrubbing is adequately demonstrated. See our discussion of the representativeness of test data used to demonstrate the statutory requirement of achievability in National Lime Association v. EPA, 627 F.2d 416, 432-34 (D.C.Cir.1980). See also Portland Cement Ass’n v. Ruckelshaus, 486 F.2d 375, 392 (D.C.Cir.1973); Int’l Harvester Co. v. Ruckelshaus, 478 F.2d 615, 647 (D.C.Cir.1973); American Petroleum Institute v. EPA, 540 F.2d 1023, 1038 (10th Cir. 1976), cert. denied, 430 U.S. 922, 97 S.Ct. 1340, 51 L.Ed.2d 601. EPA itself has been aware that “the major uncertainty which exists with dry SO2 removal technology is the absence of experience at large-scale facilities.” Memorandum from F. Princiotta to D. Goodwin, “Application of Dry SO2 Removal Technology to Western Coal Fired Utility Plants,” 2, J.A. 4497, 4498 (EPA, July 27, 1978) (Ad.Doc. No. II-B-102). And even the testing at the pilot scale has been limited as noted by a later survey by the same technical expert at EPA. EPA Memorandum from F. Princiotta to D. Goodwin, “Status of Dry S02 Control Processes” 3, J.A. 4721, 4725 (EPA, Feb. 26, 1979) (Ad.Doc. No. IV-B-34). We see no basis on this record which would justify extrapolating from the pilot scale data to the conclusion that dry scrubbing is adequately demonstrated for full scale plants throughout the industry. See and compare our discussion of the representativeness of EPA’s pilot scale data for bag-houses, text at nn.364-94 infra.
      
      Furthermore, there is no test data at all available for the performance of dry scrubbers burning low alkaline coal, which comprises roughly half of the supply of low sulfur coal, and is more difficult to clean than low sulfur coal with high alkalinity. See, e. g., 44 Fed.Reg. at 33523, col. 1; Ad.Doc. No. V-B-l, supra, at 3- 62 to 3-68, J.A. at 2666-72. Both of the fuels used in the pilot plants with dry scrubbers, North Dakota lignite and Powder River Basin sub-bituminous coal, are highly alkaline and thus are relatively easier to clean with a dry scrubber than coals with lower alkaline content. Id. See our discussion of the issue of low alkaline coal, text at nn.181-84 infra.
      
      For these reasons, it would be premature to conclude that dry scrubbing is adequately demonstrated technology.
     
      
      . Ad.Doc. III-B-4, supra note 125, at 4-23 to 4- 25; J.A. at 2333-35; Ad.Doc. No. V-B-l, supra note 75, at 2-90; 3-60 to 3-76; J.A. at 2464, 2664-80.
     
      
      . 43 Fed.Reg. at 42158, col. 3.
     
      
      . Public Hearing, supra note 94, at 92-94, 102, J.A. at 3064-66, 3074 (statement of Joseph Greene, Public Service Co. of Colorado); at 226, J.A. at 3078 (Statement of James Bechtold, Northern States Power); at 256-69, J.A. at 3081-94 (statement of B.G. Godec, City of Colorado Springs, Department of Public Utilities); see also Comment of Colorado Dept. of Health, J.A. at 4531-58 (Ad.Doc. No. IV-D-212); Comment of Washington Public Power System, J.A. at 4577-80 (Ad.Doc. No. IV-D-330). EPA’s interpretation of these comments is at 45 Fed. Reg. at 8216, cols. 2-3.
     
      
      . 44 Fed.Reg. at 33604, col. 3.
     
      
      . 44 Fed.Reg. at 33608, col. 1-33609, col. 2 (Tables 1-5, shown as Figures 4-8 in the appendix to this opinion). For example, the model projected that in 1995, variable control with dry scrubbing would produce lower national emissions than variable control with wet scrubbing (20.5 million tons versus 20.6 million tons) while utilizing more plant capacity (537 GW versus 533 GW) and generating substantially less sludge (41 million tons versus 50 million tons). The regional emission levels were roughly comparable under both versions of the variable control option. The model projected that the regional emissions of dry scrubbing as compared to wet scrubbing would be lower in the East (9.7 million tons versus 9.8 million tons), higher in the Midwest (8.0 million tons versus 7.9 million tons), lower in the West South Central (1.7 million tons versus 1.8 million tons), and the same in the West (1.1 million tons). Turning to the forecast energy impacts, national coal production should be essentially the same under either the dry or wet assumptions (1,752 million tons versus 1,770 million tons). The amount of western coal shipped East with dry scrubbing would be slightly less than with wet scrubbing (70 million tons versus 71 million tons), and the total oil consumption would be the same (1.6 million barrels per day). Finally, all of the projected costs were lower under the dry scrubbing assumption than under the wet scrubbing assumption at the level of variable control: i. e., average monthly residential bills ($54.05 per month versus $54.30 per month), indirect consumer costs ($1.20 per month versus $1.30 per month), cumulative incremental capital expenditures by utilities ( — 1 billion dollars versus 10 billion dollars — j.e., under the dry scrubbing assumption utilities would spend 1 billion dollars less than they would under the former standard while under the wet assumption they would spend 10 billion dollars more), incremental annualized costs (3.3 billion dollars versus 3.6 billion dollars), and the incremental cost of sulfur dioxide emission reduction ($1,036 per ton versus $1,163 per ton). Since variable control using only wet scrubbers is preferable to full control using only wet scrubbers, and since EPA’s figures show that variable control with dry scrubbing is preferable to variable control with wet scrubbing, it follows that variable control with dry scrubbing is more desirable than full control with wet scrubbing alone.
     
      
      . Id. at 33592, col. 1.
     
      
      . Id. at 33582, col. 3.
     
      
      . Id. But see Ackerman & Hassler, supra, note 8, at 1536-56 and esp. 1554.
     
      
      . 44 Fed.Reg. at 33582, col. 3.
     
      
      . Id. at 33583, cols. 1-2. At argument counsel for EPA stated that 70 percent appeared to be a “convenient cut” between control levels previously subjected to the agency’s computer analysis. The 70 percent figure was first suggested, however, by dry scrubbing technology. This “idea” or “hunch” when tested turned out to be the best of all standards run through the analysis. EPA was unable to offer “a good answer why the figure was not 67 percent, or alternatively 72 percent, or some other specific percent.”
     
      
      . E. g.. Reply Brief for Petitioner Sierra Club at 2; Brief for Petitioner Sierra Club at 24-27.
     
      
      . “For example, if a source chose to employ wet technology a 70 percent reduction requirement serves to substantially reduce the energy impact of operating wet scrubbers in low-sulfur coals. At this level of wet scrubber control, a portion of the untested flue gas could be used for plume reheat so as to increase plume buoyancy, thus reducing if not eliminating the need to expend energy for flue gas reheat. Further, by establishing a range of percent reductions, a variable approach would allow a source some flexibility particularly when selecting intermediate sulfur content coals. Finally, under a variable approach, a source could move to a lower sulfur content coal to achieve compliance if its control equipment failed to meet design expectations.” 44 Fed.Reg. 33583, cols. 1-2.
     
      
      . Id. Sierra Club also incorrectly believes that the modeling results “demonstrate that variable control based on wet scrubbing is unquestionably inferior to the full control option, and variable control must therefore rise or fall solely on the basis of EPA’s analysis of the dry scrubber issue.” Brief for Petitioner Sierra Club at 23-24.
      According to Sierra Club, the cost differential between the 33 percent minimum standard which EPA rejected and the 70 percent minimum standard which the agency adopted (0.5 billion dollars) is “virtually identical” to the differential between the 70 percent minimum standard adopted and the 90 percent minimum standard Sierra Club favors but EPA also rejected (0.4 billion dollars). “On the other hand, EPA expressed concerns about higher emissions (1 million tons annually) under the 33% versus the 70% option. But the 70% standard would allow 17 million more tons of SO2 annually than would full controls — 17 times the level the agency deemed important.” Id. at 24 (referring to Tables 2-4 at 44 Fed.Reg. 33608-09). See figures 5-7 in the appendix to this opinion.
      However, “a glance at the wet scrubbing figures” stated in the tables does not reveal that “full controls would result in far less emissions” than variable control but instead that Sierra Club misread the tables. The figure listed by EPA for total national emissions under the variable control option with wet scrubbing is the same as the amount reported for the full option (20.6 million tons) and not seventeen million tons greater as Sierra Club erroneously states.
      Consider the following table from 44 Fed. Reg. 33608, cols. 2-3:
      
        
      
      
        
        
      
      a Results of joint EPA/DOE analyses completed in May 1979 based on oil prices of $12.90, $16.40, and $21.00/bbl in the years 1985, 1990, and 1995, respectively.
      13 With 520 ng/J maximum emission rate.
      0 Plants subject to existing State regulations of the current NSPS of 1.2 lb SO2/million BTU.
      a Based on wet S02 scrubbing costs.
      0 Based on dry S02 scrubbing costs where applicable.
      f Plants subject to the revised standards.
      (Emphasis supplied.) Note that “Total National Emissions” predicted for 1995 are 20.6 million tons for both full control and variable control assuming that wet scrubbing alone will be utilized. Apparently, Sierra Club has transposed lines from the table, twice — once vertically and once horizontally. Sierra Club has mistakenly listed the figures for “Total Coal Capacity” in place of the correct figures for “Total National Emissions,” Brief for Petitioner Sierra Club at 23-24, and then in order to arrive at a difference of 17 million tons between variable and full control must have compared the figures listed in the “Dry” columns instead of the figures listed in the “Wet” columns as would have been appropriate. Ironically, a difference of 17 million tons in total coal capacity under variable control assuming the use of dry scrubbing reinforces selecting this control option. Thus, the data supports rather than refutes EPA’s finding that variable control “produces emissions that are equal to or lower than the other options.”
      We have already disposed of Sierra Club’s additional argument that the rerun modeling analysis performed during the pendency of the petitions for reconsideration demonstrated that full control was preferable. See text at nn. 139-142 supra.
      
       
      
      . 44 Fed.Reg. at 33583, col. 3.
     
      
      . 42 U.S.C. § 74110).
     
      
      . Id.
      
     
      
      . One of the enumerated purposes of section 111 was to “create incentives for new technology.” Conference Committee Statement of Intent, supra note 49. Remarks of Sen. Muskie, supra note 50; see also Sen. Muskie’s remarks at 123 Cong.Rec. 18022-23 (1977), 3 L.H. at 728.
      The House Committee Report stated:
      The committee, in establishing standards of performance based upon emission reduction realizable with the best technological system of continuous emission reduction, believes that it is prudent public policy to require achievement of the maximum degree of emission reduction from new sources, while encouraging the development of innovative technological means of achieving equal or better degrees of control.
      
      (Emphasis supplied.) H.R.Rep.No.294, supra, at 189, U.S.Code Cong. & Admin.News at 1267, 4 L.H. at 2656.
      The Senate Committee Report stated that section 111 was intended “to assure the use of available technology and to stimulate the development of new technology." S.Rep.No.127, supra note 114, at 171, 3 L.H. at 1391. (Emphasis supplied.) The Senate Report continued:
      
        Throughout this bill there is a philosophy of encouragement of technology development. It is an encouragement to induce, to stimulate, and to augment the innovative character of industry in reaching for more effective, less-costly systems to control air pollution.
      
        Id. at 18, 3 L.H. at 1392 (emphasis supplied).
     
      
      . In addition to the mandated consideration of the factors enumerated in section 111(a) which we believe encompass technological innovation, section 317 of the Act requires EPA to perform an analysis of proposed NSPS which includes inter alia an assessment of whether the costs of compliance will vary depending on “the development of less expensive, more efficient means or methods of compliance ...” 42 U.S.C. § 7617(c)(1)(B).
     
      
      . 42 U.S.C. § 741 l(j)(l)(A)(ii).
     
      
      . For example, section 111(h) which allows EPA to impose, under certain circumstances, specific design, equipment, or work practice standards is made the exclusive statutory provision governing this subject. Section 111(b)(5) explicitly restricts EPA’s discretion to impose such standards under section 111(a):
      Except as otherwise authorized under subsection (h) of this section, nothing in this section shall be construed to require, or to authorize ... any new or modified source to install and operate any particular technological system of continuous emission reduction
      42 U.S.C. § 7411(b)(5).
     
      
      . EPA noted that lll(j) waivers were inadequate incentives for certain high-capital, front-end control technologies both at the time of the proposed rule, 43 Fed.Reg. at 42157, col. 3-42158, col. 1, and at the time the final rule was promulgated, 44 Fed.Reg. at 33591, col. 2.
     
      
      . E. g., Ad.Doc. No. II-A-2, supra note 157, at 1, J.A. at 4497 in which EPA’s technical staff reported:
      [I]t appears that dry S02 removal is capable of removing 85 percent (24 hour average) of the potential sulfur oxide emissions from the combustion products of low sulfur Western coals using either lime or soda ash.
      [I]t appears that 85 percent reduction in S02 emissions using lime as the reactant is technically and economically feasible for coals containing less than 1.5 percent sulfur. [Approximately 90 percent of Western coal reserves contain 1.5 percent or less sulfur.] Using a soda ash material, it appears that an 85 percent reduction in S02 emissions is technically and economically feasible for all Western coal reserves.
      A later EPA memorandum by the same author stated that “[l]imited data suggest that up to 90 percent SO2 removals (long term average) may be achievable” and noted that two of the three full scale systems on order are designed for removal efficiencies greater than 70 percent. (The Basin Electric Laramie River No. 1 Plant is designed for 90 percent removal efficiency, the Basin Electric Antelope Valley No. 1 Plant is designed to achieve 78 percent removal efficiency, and the third plant, the Otter Tail Power Coyote No. 1 Plant is designed to achieve 50 percent removal efficiency. The plants are designed to comply with minimum state emission limitations). Ad.Doc. No. IV-B-34, supra note 157, at 3-4, J.A. at 4724-25.
      Studies prepared for EPA by private contractors reported achievement of removal efficiencies of 90 percent or more by various types of dry scrubbers. Ad.Doc. No. II--A-71, supra note 69, at 3-331, 3-340, J.A. at 845, 854; Flue Gas Desulfurization Systems: Design and Operating Considerations, Vol. II: Technical Report, 2-14, J.A. 1003, 1036 (EPA Pub.No. 600/7-78-030b, March 1978) (Ad.Doc. No. IIA-75). See also Letter from J. Brecher to D. Costle, 2-3, J.A. 5387, 5388-89 (Supplement to Sierra Club Petition for Reconsideration, Jan. 14, 1980) (Ad.Doc. No. VI-B-27) which contains information obtained from EPA pursuant to a Freedom of Information Act Request that shows that there were at least two plants (in EPA region VIII) which voluntarily switched from wet scrubbing to dry scrubbing and proposed to meet a removal efficiency standard of 90 percent.
      EPA argues that such evidence of high removal efficiency (greater than 70 percent) must be discounted because the data is derived from plants burning high alkaline coal. Brief for Respondent EPA at 75-79; see text at nn. 180-84 & n. 184 infra.
      
     
      
      . Calculated on a 24 hour basis without credit for full treatment or other control techniques. 43 Fed.Reg. at 42160, col. 1. Somewhat ironically, EPA explained that it was necessary to lower the standard from the 85 percent proposal less than a year later “when it was found that the development of dry SO2 controls . . . progressed rapidly during the past 12 months.” 44 Fed.Reg. at 33582, col. 3. EPA does not identify the new development but rather merely refers to information which was already on the record at the time of the proposal. See 43 Fed.Reg. at 42160, col. 1.
     
      
      . In the background document supporting the final NSPS EPA stated:
      Since all of the published test results are for alkaline coals, the uncertainty in the stoichiometric ratio which is required to achieve a 70 percent reduction for nonalkaline coals is larger than for alkaline coals. This uncertainty could have a significant impact on the [operating and maintenance] costs because the reagent and waste disposal costs are about 70-85 percent of the operating and maintenance requirements [of a dry scrubber],
      Ad.Doc. No. V-B-l, supra note 75, at 3-68, J.A. at 2672.
      Thus in the preamble to the final rule EPA concluded;
      [a] requirement of 90 percent reduction in potential S02 emissions would be likely to constrain the full development of this [dry scrubbing] technology by limiting its potential applicability to high alkaline content, low-sulfur coals. For non-alkaline, low-sulfur coals, the certainty of economically achieving a 90 percent reduction level is markedly reduced. In the face of this finding, it would be unlikely that the technology would be vigorously pursued for these low alkaline fuels which comprise approximately one half of the Nation’s low-sulfur coal reserves.
      44 Fed.Reg. at 33583, col. 1.
     
      
      . Reply Brief for Petitioner Sierra Club at 10.
     
      
      . See, e. g., Ad.Doc. No. II-A-75, supra note 179, at 5-12, J.A. at 1120 (discusses “Effect of Coal Properties on FGD Systems” and states “Due to the natural variability of fly ash quanlity and alkali content a supplemental feed of limestone or lime is generally needed for effective chemical control of the system”).
     
      
      . Based on pilot scale testing at four plants EPA graphed a relationship between percent reduction and stoichiometric ratio for alkaline coal. Ad.Doc. No. V-B-l, supra note 75, at 3-62 to 3-65, J.A. at 2666-69, Figure 3-27. The graph is shown as Figure 12 in the appendix to this opinion. On only the basis of what EPA identifies as “proprietary data” the agency concluded that if non-alkaline coal was used, “the stoichiometric ratio would increase dramatically, by as much as a factor of two. ...” Id. at 3-62, J.A. at 2666.
      EPA’s economic analysis of dry scrubbing is contained in the final background document, Ad.Doc. No. V-B-l, supra note 75, at 3-66 to 3-75, J.A. at 2670-79, and included in the materials distributed to the panel at argument. See also Attachments to EPA Memorandum from W. Barber to Files (Documenting May 1, 1980 meeting in S. Eizenstat’s White House Office), J.A. at 4993, 5801-06 (EPA, May 24, 1980) (Ad.Doc. No. IV-E-21). (The relevant tables and diagrams are shown as Figures 13 through 18 in the appendix to this opinion.)
      These materials are deficient in several respects. They are inaccurate (e. g., Figure 3-28 should read “D” instead of “C” on the horizontal axis) and incomplete (e. g., there is no economic comparison of wet scrubbing and dry scrubbing at the 90 percent or full control level and there is no explanation of how the materials were compiled). At any rate the tables and diagrams amount to little more than visual depictions of EPA’s conclusory statements and do not reflect calculations, tests, and existing data. In fact, the economic materials contain no citations whatsoever as to sources of the information represented in the figures. EPA’s background document in this case lists “References” as footnotes at the end of the chapter, but the single reference applicable to the section on the economics of dry scrubbing did not attempt to document the tables and diagrams contained in the section. If the supporting data is buried elsewhere in the voluminous record, EPA has not called it to our attention. See Natural Resources Defense Council v. Nuclear Regulatory Comm’n, 547 F.2d 633, 646 (D.C.Cir.1976); Home Box Offíce, Inc. v. FCC, 567 F.2d 9, 35 (D.C.Cir.1977); Asarco, Inc. v. EPA, 616 F.2d 1153, 1162-63 (9th Cir. 1980) (criticizing agency’s conclusory statements and superficial inquiry). U. S. Lines v. FMC, 584 F.2d 519, 533 (D.C.Cir.1978) (admonishing agency for “blind references”). Ackerman & Hassler, supra note 8, at 1554 indicate that EPA relied on “sketchy cost data provided by its Office of Resource and Development.”
      In fact, data in documents prepared by EPA less than one month before issuance of the final rule seemed to point in the opposite direction. E. g., “Basin Electric’s Involvement With Dry Flue Gas Desulfurization,” EPA Memorandum from D. Hawkins to S. Eizenstat, Attachment D, J.A. 4863, 4873 (EPA, May 2, 1980, docketed June 1, 1980) (Ad.Doc. No. VI-C-268). Economic evaluations of wet versus dry scrubbing showed that dry scrubbing was more economical than wet scrubbing even when reagent costs increased dramatically. In one case dry scrubbing was more economical even though total projected reagent costs increased from approximately 9 to almost 49 million dollars (over 35 years). Id. at Table 8, J.A. at 4890. In another case total reagent costs were actually lower for dry scrubbing than for wet scrubbing. Id. at Table 7, J.A. at 4889. Considerable savings associated with dry scrubbing such as lower capital, replacement, and manpower costs were shown to offset costs of extra reagent. Compare id. at Table 2, J.A. at 4884, with id. at Table 8, J.A. at 4890.
      In addition, a comparison of the total lifetime costs of the two plants for which economic data were reviewed suggests that on a per megawatt basis, dry scrubbing at 90 percent removal efficiency at the larger plant will be less expensive than dry scrubbing to only 78 percent removal efficiency at the smaller plant. Although the significance of this particular comparison may be limited by possible economies of scale and other variables not accounted for, it hardly instills confidence in the reasonableness of EPA’s final economic analysis of the performance of dry scrubbing. See also EPA Memorandum from J. Haines to J. Farmer, Table 8 in Attachment No. 2, Table 2 in Attachment No. 4 (EPA, Docketed May 4, 1979) (Ad. Doc. No. IV-B-66, not included in Joint Appendix).
     
      
      . See n.160 supra. One witness at the hearing stated:
      We also have reviewed articles in scientific literature which describe [dry scrubbing] technology and the comments of EPA included in the preamble to these proposed standards. All of this documentation concludes that dry removal technology is capable of approximately 70 percent removal, not 85 percent as proposed by EPA.
      An 85 percent standard clearly would require the use of a wet scrubber.
      Statement of George Greene, Public Service Co. of Colorado, Hearing on Proposed Standards (EPA Dec. 13, 1978), 88, 92-93, J.A. 3061, 3064-66. See Comments of Rep. Patricia Schroeder, 2, J.A. 4687, 4689 (Jan. 12, 1979) (Ad.Doc. No. IV-D-590).
     
      
      . E. g. Initial Comments of the Electric Utilities, 93-94, J.A. 3299, 3674-75 (Dec. 15, 1978) (Ad.Doc. No. IV-D-491a); Supplemental and Reply Comments of the Electric Utilities, 4, J.A. 3717, 3727 (Jan. 15, 1979) (Ad.Doc. No. IV-D-611a).
     
      
      . See nn. 179, 184 supra. Also, permit applications filed and granted in EPA’s regional offices showed that plants were voluntarily switching from wet scrubbing to dry scrubbing and forecasting achievement of 90 percent removal efficiency. See Ad.Doc. No. VI-B-27, supra note 179, at 2-3, J.A. at 5388-89.
     
      
      . Oklahoma Gas & Electric Co. applied for a permit to EPA Region VI for construction of its Sooner Station No. 3 with a wet scrubber designed to achieve only 70 percent removal efficiency. The company rejected the use of dry scrubbing equipment. Prevention of Significant Deterioration Application, Sooner Generating Station, Attachment C, Brief for Petitioner Sierra Club (obtained by Sierra Club pursuant to a Freedom of Information Act Request, Feb. 19, 1980).
     
      
      . Ad.Doc. No. III-B-3, supra note 9, at 1850.
     
      
      . Sierra Club’s Petition for Reconsideration, 2, 4, 13, J.A. 5455, 5456, 5458, 5467 (July 18, 1979) (Ad.Doc. No. VI-A-3).
      The Electric Utilities also complained that there was insufficient time to comment on the dry scrubbing aspects of the phase three analysis, along with the supporting data entered into the record after the close of the public comment period. Electric Utilities’ Petition for Reconsideration, 9, 21, J.A. 5133, 5137, 5143 (Aug. 10, 1979) (Ad.Doc. No. VI-A-5).
     
      
      . 42 U.S.C. § 7607(d).
     
      
      . Id.
      
     
      
      . As this court stated in Weyerhaeuser v. Costle, a case brought under the Clean Water Act, an agency “need not subject every incremental change in its conclusions after each round of notice and comment to further public scrutiny before final action.” 590 F.2d 1011, 1031 (D.C.Cir.1978). However public notice of a change in the agency’s approach is required where:
      [T]he agency’s final conclusions are far from the “logical outgrowth" of the preceding notice and comment process ... and instead are the result of controversial and uncommented upon data and calculations. Given the lengths that the agency must travel to justify its revisions between the interim and final stages, we cannot be sure that further and ultimately convincing public criticism of those changes would not have been forthcoming had it been invited by the agency.
      
        Id. And see National Tour Brokers Ass’n v. United States, 591 F.2d 896 (D.C.Cir.1978); U. S. Lines v. FMC, 584 F.2d 519, 533-35 (D.C.Cir.1978); Home Box Office, Inc. v. FCC, 567 F.2d 9, 34-35 (D.C.Cir.1977); Portland Cement Ass’n v. Ruckelshaus, 486 F.2d 375, 392-95 (D.C.Cir.1973).
     
      
      . 45 Fed.Reg. at 8215, col. 3.
     
      
      . 43 Fed.Reg. at 42154, col. 1.
     
      
      . Id.
      
     
      
      . E. g., Minutes of National Air Pollution Control Techniques Advisory Committee, 34, J.A. 2873, 2906 (Dec. 1977) (Ad.Doc. No. II-B-72); Letter from Hunton & Williams to D. Goodwin, 8-14, J.A. 4425, 4433-39 (Jan. 6, 1978) (Ad.Doc. No. II-D-180).
     
      
      . See 44 Fed.Reg. at 33596, col. 2-33597, col. 3; and 45 Fed.Reg. at 8216, col. 1-8222, col. 2 (summarizing and responding to comments on the percentage reduction standard).
     
      
      . 43 Fed.Reg. at 42161, col. 2.
     
      
      . Id. at col. 1.
     
      
      . 43 Fed.Reg. at 57835, cols. 1-2, & 57837-59 (Tables 1 to 8). As Sierra Club recognizes these prepromulgation sliding scale options “had nothing to do with the dry scrubbing issue.” Brief for Petitioner Sierra Club at 11.
     
      
      . 45 Fed.Reg. at 8220, col. 2-8221, col. 2.
     
      
      . See, e. g., Comments of Sierra Club 6-10, 13-18, J.A. 3095, 3102-06, 3109-14 (Dec. 12, 1978) (Ad.Doc. No. IV-F-21), Comments of EDF/NRDC at V-l to V-24, J.A. 4695 (pages not in J.A.) (Jan. 15, 1979) (Ad.Doc. No. IV-D-631); UARG Initial Comments, Appendix E, J.A. 3299, 3577-3676 (Dec. 15, 1978) (Ad.Doc. No. 1V-D — 491).
     
      
      . Compare Sierra Club’s Comments, Ad.Doc. No. IV-F-21, supra note 203, at 13-18, J.A. 3095, at 3109-14 with Brief for Petitioner Sierra Club at 15-16, 47-51.
     
      
      . See 43 Fed.Reg. at 57834, col. 2-57836, col. 1; 45 Fed.Reg. at 8217, col. 2-8222, col. 1.
     
      
      . Ad.Doc. No. II-B-72, supra note 197, at 19, J.A. at 2873, 2891.
     
      
      . See text at nn. 157-59 supra.
      
     
      
      . Ad.Doc. No. IV-D-491, supra note 203, Part Two at 7, Appendix E at 92-93, J.A. at 3361, 3674-75.
     
      
      . Electric -Utilities’ Supplemental and Reply Comments, at 5, J.A. at 3727.
     
      
      . See nn. 94, 160 supra.
      
     
      
      . Ad.Doc. No. IV-D-631, supra note 203, at 11-38, V-l, J.A. 4695 (pages not in J.A.).
     
      
      . See generally Ad.Doc. No. IV-F-21, supra note 203.
     
      
      . In reality EPA was not operating in an insulated bureaucratic environment. “[0]ut-siders were informed of agency policy through agency leaks or by BNA’s Environment Reporter. In addition the EPA routinely submitted its proposals to other executive offices for review.” Ackerman & Hassler, supra note 8, at 1542 & n. 312.
     
      
      . Letter from R. Ayres, for NRDC and R. Rauch, for EDF, to D. Costle 1-2, J.A. 4815-16 (Ad.Doc. No. IV — D — 759).
     
      
      . Letter from G. Freeman, for the Electric Utilities, to D. Costle 1-2, J.A. 4833-34 (April 22, 1979)(Ad.Doc.No. IV-D-761).
     
      
      . See n. 184 supra.
      
     
      
      . See nn. 157, 179, 184 supra.
      
     
      
      . 42 U.S.C. § 7607(d)(8).
     
      
      . We recognize, of course, that EPA was under a court imposed deadline to promulgate the final standard. But time restraints do not jettison the flexibility and capacity of re-examination that is rooted in the administrative process. Int’l Harvester Co. v. Ruckelshaus, 478 F.2d 615, 632 (D.C.Cir.1973).
     
      
      . The achievability of 90 percent reduction on coals with sulfur content less than 6.0 lbs./MBtu is not in dispute. Under the variable standard less than 90 percent reduction is required when these coals are combusted. Seventy-five percent of the Nation’s coal reserves will not have to meet the 90 percent standard. 45 Fed.Reg. at 8223, col. 3.
      Compliance with the standard is required for every 30 day period of boiler operation. Therefore, each day of boiler operation begins a new 30 day compliance period. E. g„ 44 Fed.Reg. at 33609, col. 3.
     
      
      . 42 U.S.C. § 7607(d).
     
      
      . Brief for Respondent EPA at 59.
     
      
      . Id at 59-60.
     
      
      . 43 Fed.Reg. at 42155, col. 2, 42158, col. 3.
     
      
      . Id. at 42158, col. 3, 42160, cols. 1-2, 42173, cols. 1-2.
     
      
      . Ad.Doc. No. III-B-4, supra note 125, at 4-33, J.A. at 2343.
     
      
      . 44 Fed.Reg. at 33581, col. 3.
     
      
      . Id. at 33582, col. 2.
     
      
      . Id. at 33592, col. 1.
     
      
      . Id. at 33593, cols. 1-2.
     
      
      . See nn.225, 226, supra; Ad.Doc. No. III-B-3, supra note 9, at 3-2, J.A. at 1784.
     
      
      . See “Physical Coal Cleaning for Utility Boiler SO2 Emission Control,” Interagency Energy Research and Development Program Report (Batelle), J.A. at 293 (EPA Pub.No. 600/7-78-034, Feb. 1978) (Ad.Doc. No. II-A-62); “Particulate and Sulfur Dioxide Control Costs for Large Coal-Fired Boilers,” (Pedco), X, 6-1, J.A. at 405, 414, page not in J.A. (EPA Pub.No. 450/3-78-007, Feb. 1978) (Ad.Doc. No. II-A-64); “Review of NSPS for Coal-Fired Utility Boilers, Volume I: Emissions and Nonair Quality Environmental Impacts,” Environmental Impacts Interagency Energy/Environment Program Report, J.A. 441 (EPA Pub.No. 600/7-78-155a, Aug. 1978) (Ad.Doc. No. II-A-67); “FGD System Capabilities for Coal Fired Steam Generators Vol. II Technical Report” (Pedco), 2-11 to 2-16, J.A. 477, 507-512 (EPA Pub.No. 600/7-78-032b, Mar. 1978) (Ad.Doc. No. II-A-71); “Controlling SO2 Emissions From Coal-Fired Steam-Electric Generators: Water Pollution Impact (Volume II, Technical Discussion),” (Radian Corp.), J.A. 1211 (EPA Pub.No. 600/7-78-045b, Mar. 1978) (Ad.Doc. No. II-A-79); “Effects of Alternative New Source Performance Standards for Coal-Fired Electric Utility Boilers on the Coal Markets and on Utility Capacity Expansion Plans” (Draft) (ICF), J.A. 1217 (Sept. 1978) (Ad.Doc. No. II-A-90); Ad. Doc. No. III-B-3, supra note 9, at 4-7 to 4-42, J.A. at 1793-828; Ad.Doc. No. III-B-4, supra note 125, at 4-31 to 4-34, J.A. 2251, 2341-44.
     
      
      . Ad.Doc. No. II-A-62, supra note 232, at 3, J.A. at 308. An emission ceiling of 0.4 lbs./MBtu amounts to a 90 percent reduction for coals with sulfur content of 4 lbs./MBtu.
     
      
      . Id. at 4, J.A. at 309. The report did not focus on percentage reduction requirements because none had been specified at the time the study was prepared.
     
      
      . Comments summarized in Ad.Doc. No. VB-l, supra note 75, 2-143 to 2-145, J.A. at 2517-19. 44 Fed.Reg. at 33593, cols. 1-2.
     
      
      . Ad.Doc. No. IV-D-631, supra note 203, at IV-11 to IV-12, J.A. at 4702-03.
     
      
      . Ad.Doc. No. IV-D-611a, supra note 186, at 57, J.A. at 3781.
     
      
      . 43 Fed. Reg. at 57834, col. 3.
     
      
      . The April 5, 1979 meeting is discussed in detail in our review of EDF’s appeal of the 1.2 lbs./MBtu emission ceiling. EPA indicated in advance that coal washing would be a primary subject for discussion at the April 5 meeting. E. g., Letter from J. Haines, for EPA to G. Freeman, J.A. at 4765, (Mar. 30, 1979) (Ad.Doc. No. IV-B-57); Letter from J. Haines, for EPA to J. Mullen, for NCA, J.A. at 4775 (Mar. 30, 1979) (Ad.Doc. No. IV-E-10).
     
      
      . Minutes of April 5, 1979 meeting (with attachments) J.A. at3119&5513 (docketed May 2, 1979) (Ad.Doc. No. IV-E-11); Memorandum from J. Kilgro to J. Haines (with attachments), J.A. at 4787 (EPA, April 9, 1979, docketed May 2, 1979) (Ad.Doc. No. IV-E-12).
     
      
      . Letter from G. Freeman, for Electric Utilities to D. Costle, J.A. at 4727 (Mar. 2, 1979) (Ad.Doc. No. IV-D-744); Letter from G. Freeman, for Electric Utilities to D. Costle, J.A. at 4833 (April 23, 1979) (Ad.Doc. No. IV-D-761); Letter from G. Freeman, for the Electric Utilities to D. Costle, J.A. at 4943 (May 18, 1979) (Ad.Doc. No. IV-D-848). '
     
      
      . Letter from C. Bagge, for NCA to D. Costle (with attachments), J.A. at 4777 (April 6, 1979) (Ad.Doc. No. IV-D-756).
     
      
      . Letter from R. Rauch and R. Ayres, for EDF, J.A. at 4809 (April 19, 1979) (Ad.Doc. No. IV-D-763).
     
      
      . Ad.Doc. No. IV-D-744, supra note 241, at 2, J.A. at 4728.
     
      
      . Id. at 8, J.A. at 4734.
     
      
      . Ad.Doc. No. IV-D-761, supra note 241, at 1, J.A. at 4833.
     
      
      . Ad.Doc. No. IV-D-848, supra note 241, at 2, J.A. at 4944.
     
      
      . See nn. 244-47 supra.
      
     
      
      . Section 307(d)(6)(A)(ii) requires the promulgated rule to be accompanied by “an explanation of the reasons for any major changes in the promulgated rule from the proposed rule.” 42 U.S.C. § 7607(d)(6)(A)(ii).
     
      
      . “A median is a level that divides the data points in half; one half are above the median and one half are below it.” Brief for Respondent EPA at 33 n.24.
     
      
      . 45 Fed.Reg. at 8222, col. 3-8223, col. 1. See n. 255 infra.
      
     
      
      . Id. at 8223, col. 1. In fact, EPA announced that “[ejven if a new FGD system attained only 85 percent efficiency (30-day rolling average), a 90 percent reduction in potential S02 emissions can be met when sulfur reduction credits [for coal washing and ash retention] are considered.” Id.
      
     
      
      . 44 Fed.Reg. at 33592, col. 2.
     
      
      . Brief for Respondent EPA at 37-38, 45 Fed. Reg. at 8223, col. 1.
     
      
      . “ ‘Autocorrelation’ is a statistical term which describes the relationship (or correlation) between the values of a variable measured at different points in time. In the context of FGD operation, autocorrelation refers to the tendency of a given day of FGD performance to be related to performance of the system on the previous day.” Brief for Petitioner APCO at 28 n.78. See Electric Utilities’ Petition for Reconsideration 12-13, J.A. at 5133, 5138A-5139 (Aug. 10, 1979) (Ad.Doc. No. VI-A-5); 45 Fed. Reg. at 8225, cols. 1-3.
     
      
      . 45 Fed.Reg. at 8225, col. 1.
     
      
      . Id at col. 3.
     
      
      . Brief for Respondent EPA at 33.
     
      
      . E. g., 45 Fed.Reg. at 8225, col. 2. See Ackerman & Hassler, supra note 8, at 1542 n.317 (“During the modeling process a requirement that a scrubber reduce emissions by an average of 85% every day was generally considered to be equivalent to a requirement that it reduce emissions by an average of 90% over a longer period such as a month or year.”).
     
      
      . 44 Fed.Reg. at 33592, cols. 2-3; Ad.Doc. No. III — B — 4, supra note 125, at 4-6 to 4-11, J.A. at 2316-23.
     
      
      . Ad.Doc. No. III — B — 4, supra note 125, at 4-18, J.A. at 2328. This system was designed for 90 percent removal efficiency. Id. at 4-7, Table 4-1, J.A. at 2317.
     
      
      . Ad.Doc. No. III-B-4, supra note 125, at 4-3 to 4-4, J.A. at 2313-14.
     
      
      . 44 Fed.Reg. at 33592, cols. 1-3. See also “Double Alkali (Soda Lime) Scrubbing” & “Magnesium Oxide Scrubbing,” FGD Systems: Design and Operating Considerations. Volume II. Technical Report (Bechtel), 3-20 to 3-32, J.A. at 1003, 1060-72 (EPA 600/7-78-030b, Mar. 1978) (Ad.Doc. No. II-A-75).
     
      
      . See, e. g., Ad.Doc. No. II-A-71, supra note 232, at 3-10, Table 3-2, J.A. at 524. Of 12 lime/limestone systems surveyed by Pedco, only 3 were designed for over 90 percent efficiency.
     
      
      . 44 Fed.Reg. at 33592, cols. 1-3; Ad.Doc. No. III-B-4, supra note 125, at 47, Table 4-1, J.A. at 2317.
     
      
      . Conesville was rejected as a “well run” FGD system insofar as its variability was concerned.
     
      
      . 44 Fed.Reg. at 33592, cols. 1-3.
     
      
      . Brief for Respondent EPA at 39.
     
      
      . Reply Brief for Petitioner APCO at 31.
     
      
      . Ad.Doc. No. II-A-71 (Pedco Report), supra note 2$2, 3-40 to 3-66, 3-96 to 3-107, 4-30 to 4-34, J.A. at 554-80, 610-21, 902-06; Pedco, for example, stated that new systems could be designed for high efficiency by taking account of key variables including: (1) inlet sulfur dioxide concentration rate, (2) liquid-to-gas ratio, (3) scrubber gas velocity, (4) scrubber liquor inlet pH, (5) type of absorber, (6) magnesium content, and (7) type of alkali. Id at 4-3, J.A. at 902. Pedco concludes that “[t]he design and operating experience gained with first generation FGD systems has resulted, and will continue to result, in improved design and operation of subsequent installations ... even better performance can be expected as newer plants are completed.” Id at 4-1, J.A. at 873.
      Ad.Doc. No. II-A-75 (Bechtel Report), supra note 263, iii, 4-1 to 4-24, J.A. at 1007, 1073-96. The Bechtel Report defines changes that would be applied to a new facility to obtain 90 percent or greater removal “[w]here an installed full-scale FGD system has demonstrated good operation, but at lower S02 removal efficiencies (such as 60 to 85 percent).” Id. at iii, J.A. at 1007. For example, “S02 removal efficiency may be increased by increasing the liquid-togas ratio, changing pH, addition of MgO to lime/limestone scrubbers, changes in scrubber gas velocity, increasing bed heights in adsorption towers, and others.” Id. at iv, J.A. at 1008.
      Ad.Doc. No. III-B-4, supra note 125 at 4-19 to 4-23, J.A. at 2329-33.
     
      
      . E. g., at Louisville Gas & Electric Company’s Cane Run Station the addition of magnesium oxide to the lime in the FGD increased removal to 95 to 96 percent over a three day test period. Ad.Doc. No. III-B-4, supra note 125, at 4-10, J.A. at 2320. The Electric Utilities recognize that it is possible to increase FGD performance for short time periods, as with “performance acceptance testing.” E. g., Reply Brief for Petitioner APCO at 27 n.76.
      At the company’s Paddy Run Station, magnesium oxide insertion produced over 99 percent removal during two 8-hour tests. Ad.Doc. No. III- B — 4, supra.
      
     
      
      . National Lime Ass’n v. EPA, 627 F.2d 416, 438-39 (D.C.Cir.1980).
     
      
      . Ad.Doc. No. II-A-71, supra note 232, at 4-29, Table 4-8, J.A. at 901.
     
      
      . 44 Fed.Reg. at 33592, col. 3.
     
      
      . “Statement by IGCI on Proposed NSPS,” J.A. at 4559, 4561 (Nov. 17, 1978) (Ad.Doc. No. IV- D-247); EPA noted this statement at 44 Fed.Reg. at 33595, col. 1.
     
      
      . Portland Cement Ass’n v. Ruckelshaus, 486 F.2d 375, 391 (D.C.Cir.1973), cert. denied, 423 U.S. 1025, 96 S.Ct. 469, 46 L.Ed.2d 399 (1975). “Section 111 looks toward what may fairly be projected for the regulated future, rather than the state of the art at present, since it is addressed to standards for new plants. . .. The essential question was . . . whether the technology would be available for installation in new plants.” Id. See Union Electric Co. v. EPA, 427 U.S. 246, 256-57, 96 S.Ct. 2518, 2525-2526, 49 L.Ed.2d 474 (1976); Train v. Natural Resources Defense Council, Inc., 421 U.S. 60, 75, 95 S.Ct. 1470, 1479-1480, 43 L.Ed.2d 731 (1975); Forcing Technology: The Clean Air Act Experience, 88 Yale L.J. 1713 (1979).
      There are many allusions in the legislative history to the ability of scrubbers to achieve 80 to 90 percent removal efficiency. E. g., remarks of Sen. Muskie 123 Cong.Rec. 18023 (1977), 3 L.H. at 729; H.Rep.No.294, supra note 47, 89-90, 4 L.H. at 2556-7. These figures were supported by the Federal Energy Administration, the Commerce Department’s Technical Advisory Committee, and the National Academy of Sciences. Id.
      
     
      
      . Brief for Respondent EPA at 31 (citing National Lime Ass’n v. EPA, 627 F.2d 416, 432-33 (D.C.Cir.1980); AFL-CIO v. Marshall, 617 F.2d 636 (D.C.Cir.1979), vacated in part, 449 U.S. 809, 101 S.Ct. 56, 66 L.Ed.2d 12, cert. granted in part, 449 U.S. 817, 101 S.Ct. 68, 66 L.Ed.2d 19 (1980)).
     
      
      . Brief for Respondent EPA at 32.
     
      
      . EPA’s variability data base is presented and analyzed in a report prepared by Vector Research Inc., (“VRI”) Analysis of FGD System Efficiency Based on Existing Utility Boiler Data, J.A. 5019 (EPA Pub.No. 7.3-FR 79-1, November 1979) (Ad.Doc. No. VI-B-13). See esp. 3-1 to 3-11, J.A. at 5067-79, presenting variability data from eleven utility steam generating units. See also Ad.Doc. No. III-B-4, supra note 125, at 4-12 to 4 — 19, J.A. at 2322-29. See also A Review of FGD System Operation and Process Controls (Acurex Corp.), J.A. at 5087 (Dec. 1979) (Ad.Doc. No. VI-B-14); and compare with Memorandum from R. Rush to H. Nickel (Entropy’s comparison of VRI, Acurex, and Entropy variability analysis) (Jan. 25, 1979), Attachment A to Ad.Doc. No. VI-B-22 (Jan. 28, 1979), Reply Brief for Petitioner APCO at Appendix B.
      The Electric Utilities have summarized the variability data they contend are relevant to the variability determination in the petition for reconsideration, supra note 190, at Appendix B (Entropy Report) 26, Table 1, J.A. at 5204, and Reply Brief for Petitioner APCO at A-l, B-13 to B-14.
     
      
      . 45 Fed.Reg. at 8224, cols. 1-3; Ad. Doc. No. VI-B-14, supra note 279, at 1-6, J.A. 5089-94.
      There were continuously monitored data from three well-operated lime/limestone systems: Cane Run, Bruce Mansfield, and Shawnee.
      The Shawnee data on variability became available after the proposal and was discussed by EPA for the first time in the Denial of the Petition for Reconsideration although the data was put into the record in May, 1979. Shawnee is a pilot plant and Cane Run and Mansfield are commercial-scale units. Cane Run has been termed a “peak” plant and Mansfield and Shawnee were described as “base” plants. Variability at Mansfield and Shawnee was lower than at Cane Run. 45 Fed.Reg. at 8224, col. 2. The utilities claimed that the agency changed the basis for its variability assumption by introducing the Shawnee data after the final rule was promulgated and differentiating for the first time between “peak” and “base” plants. We find the agency’s explanation adequate that in discussing Shawnee at length, it was merely responding to the utilities’ own analysis of the variability of all the data base plants, and that its distinction between peak and base load plants was a refinement of its earlier analysis and did not alter its original conclusion on variability based on the Cane Run data. We do agree with the utilities that the agency does not satisfactorily define a “base” or a “peak” load plant.
     
      
      . Reply Brief for Petitioner APCO at 23, n.60, B-16, B-14. Entropy, the Electric Utilities’ consultant, like Acurex, EPA’s consultant, rejected the removal efficiency variability from the Lawrence, Mitchell, and Eddystone sites because they were not representative of high sulfur, lime/limestone sites.
     
      
      . 45 Fed.Reg. at 8224, col. 1 & 8225, col. 1 (citing Ad.Doc. No. VI-B-14, supra note 279, at 11-17, J.A. at 5099-105). The report concluded that existing FGD systems can be improved, for example, by using automatic pH control systems, full time trained operators, coal blending, and quality control of lime and limestone. id.
      
     
      
      . This contention was raised in conjunction with the Electric Utilities’ petition for reconsideration and reiterated in the appeal. Letter from H. Nickel, for Electric Utilities, to D. Cos-tie (January 28, 1980) 7-8, J.A. at 5403, 5409-10 (Ad.Doc. No. VI-B-22); Reply Brief for Petitioner APCO at 22. EPA did not address the argument either in its denial of the petition for reconsideration or in its appellate brief.
      EPA’s Supplemental Memorandum filed Feb. 3, 1981 pursuant to this court’s order of Jan. 22, 1981 and the Electric Utilities’ Response to EPA’s Supplemental Memorandum filed Feb. 17, 1981, discuss the relevance and interpretation of the Bruce Mansfield data in great detail which we do not believe necessary to recapitulate in this opinion.
     
      
      . EPA’s analysis of the Bruce Mansfield plant that is included in the background documents and reports relied only on data collected during two phases from September 14, 1977 through December 8, 1977. The original test report was drafted in January 1978. Memorandum from L. Jones & C. Sedman to D. Goodwin, “Staff Review and Comment to [Electric Utilities] Analyses of Phase III and Phase IV SO2 Data From Bruce Mansfield” (EPA, Feb. 2, 1981) (attached to EPA’s Supplemental Memorandum of Feb. 3, 1981) [hereinafter Staff Review Memorandum]. See “First Interim Report on Continuous SO2 Monitoring at Bruce Mansfield Unit 1” (EPA EMB Rep. No. 77SPP19, Jan. 1978) (Ad.Doc. No. II-A-59).
      Meanwhile the monitors at the site collected additional data from December 8, 1977 through April 1978. Id. The Electric Utilities obtained this data and submitted it for inclusion on the record three days before EPA published its denial of the petition for reconsideration. Ad. Doc. No. VI-B-22, supra note 283, at 7 n.19, J.A. at 5409 n.19 & Attachments B & C.
      The Electric Utilities and EPA agree that the data collected from December 8, 1977 until March 10, 1978 (phase three) were statistically indistinguishable from the phase one and phase two data. Ad.Doc. No. VI-B-22, supra, at 7-8, 5409-10. Supplemental Memorandum for Respondent EPA at 4 n.3. The controversy centers over the remainder of the data collected from March 17 until April 15, 1978 (phase four). The variability during phase four was higher than during phases one, two, and three. The first three phases were conducted when the Bruce Mansfield Unit No. 1 boiler was operating at a fairly even load at between 350 MW and 400 MW (about one-half load) with only three scrubber modules in service. However, in March 1978 a second stack was returned to service, and the boiler operated at levels fluctuating between 600 MW and 770 MW (between three-quarters and full load).
      The data is summarized in the following table:
      
        
      
      3 Standard deviation of Ln (l-efficiency/100).
      b Pooled estimate of efficiency variability for Phases I, II and III.
      Ad.Doc. No. VI-B-22, supra, at Attachment A, Table 2, J.A. at 5437.
      
      
      . EPA claims that the quality of the data in phases three and four is poorer than the data obtained during phases one and two because the monitors ran infrequently during the period and because EPA did not observe the plant generators. Supplemental Memorandum for Respondent EPA at 4. The Electric Utilities argue that the phase four data are at least as suitable as EPA’s other data, because the data capture rate and the monitoring (or lack of it) during that period were not unusual. Response Memorandum for Petitioner APCO at 11, & A-2 to A-5.
     
      
      . EPA’s analysis of the phase four data revealed pH control problems. Staff Review Memorandum, at 4, & Attachment A, Table 2. On one day, April 2, 1978, these problems were severe enough to conclude that the scrubber was not operating properly. On this day, scrubber module B was operated for one-half of the day with an improper pH level. [Scrubber B was below pH 6 for at least 6 hours. EPA had concluded that proper FGD operation included keeping the FGD above 7.0 preferably or at least above 6.0. See Ad.Doc. No. II-A-75, supra note 263, at 4-22, J.A. at 1094; Ad. Doc. No. II-A-71, supra note 232, at 4-32 to 4-33, J.A. at 904-05.] Id Under the promulgated standards, a plant would be expected to promptly repair or take a failed FGD system out of service to avoid a violation. In this instance, module A could have been substituted for module B. When the day of abnormal operation data is removed from the data base, the revised estimate of scrubber variation for phase four is 0.331. Id. at Table 3. This degree of variability is within the range of 0.36 predicted as worst case variability.
     
      
      . EPA believed that it was reasonable to assume that ash retention could contribute at least 10 percent sulfur removal. 45 Fed.Reg. at 8226, col. 1. There is only one study we can find on the record which examines the sulfur removal potential of ash retention and, candidly, we are not able to conclude after reading it that it justifies EPA’s 10 percent figure. “Sulfur Retention in Coal Ash,” Interagency Energy/Environment R&D Program Report, J.A. at 1229 (EPA Pub. No. 600/7-78-153b, Nov. 1978) (Ad.Doc. No. IV-A-6).
     
      
      . J. Davis, Coal Cleaning Readies for Wider Sulfur Removal Role, Chemical Engineering, 70, J.A. at 2707 (Mar. 1, 1976) (Ad.Doc. No. II — I — 182). See also Ackerman & Hassler, supra note 8, at 1480-81.
      PCC has been used for many years to reduce cost and to enhance heating value. As such, PCC is an available technology. Improvements designed to increase sulfur removal are being developed and incorporated in the technology. PCC costs vary with the type of coal and the treatment employed. ... A number of chemical and cleaning processes are in various stages of development. These are designed to achieve greater sulfur removal than PCC. However, none of these processes is commercially available at this time.
      Ad.Doc. No. II-A-62, supra note 232, at 4, J.A. at 309.
      Section 111 allows an NSPS to be based on sulfur removal techniques like coal washing since it defines “technological system of continuous emission reduction” as “including precombustion cleaning or treatment of fuels.” 42 U.S.C. § 7411(a)(7)(B). The legislative history showed that Congress intended coal washing to be considered a sulfur removal technology although use of coal washing alone would not be a suitable substitute for FGD. H.R.Rep.No.294, supra note 47, at 188-89, 4 L.H. 2655-56.
     
      
      . Ad.Doc. No. II-A-62, supra note 232, at 79-80, J.A. at 384-85; Ad.Doc. No. III-B-3, supra note 9, at 4-8 to 4-17, J.A. at 1795-803. 44 Fed. Reg. at 33593, col. 2.
     
      
      . Id.
      
     
      
      . Ad.Doc. No. II-A-62, supra note 232, at 27, 79-80, J.A. at 332, 384-85; Ad.Doc. No. III-B-3, supra note 9, at 4-9 to 4-10, J.A. at 1795-96.
      The government’s counsel erroneously state that “[p]hysical coal cleaning is capable of removing up to 70 percent of the sulfur in coal.” Brief for Respondent EPA at 57. The report they rely on, supra, states that up to 70 percent may be removed by washing of the unbonded inorganic sulfur.
     
      
      . In general, washing a high sulfur coal with a large proportion of washable pyritic sulfur crushed to a large (l'/2 inch) top size with high specific gravity (1.6) will remove less sulfur but recover more Btu’s and be more economical than crushing the same coal to smaller sizes and/or using lower specific gravities for separation with an attendant lower recovery of Btu’s.
     
      
      . The Electric Utilities offer this example but incorrectly calculate that 88 percent removal by scrubbers would be necessary because they mistakenly state that “[g]iven a coal with uncontrolled emissions of 10 Ibs./MBtu, the final rule would require 90% reduction to .9 Ibs./MBtu.” (Emphasis supplied.) Brief for Petitioner APCO at 33 n.96; Reply Brief for Petitioner APCO at 12 n.29.
      Another example is found in Ad.Doc. No. II-A-62, supra note 232, at 28, J.A. at 333: “if 50 percent of the sulfur were removed by coal cleaning, then the scrubber would have to operate at only 80 percent removal to achieve the 90 percent removal required....” See also Ad.Doc. No. III-B-3, supra, note 9, at 4-32 (Table 4-5), J.A. at 2342.
     
      
      . J. Cavallaro, Bureau of Mines, Department of the Interior, “Report of Investigations 8118” Sulfur Reduction Potential of the Coals of the United States (1976) (Ad.Doc. No. II-A-5). The 455 samples studied represented mines which provide more than 70 percent of the annual utility coal production. Id. at 3.
     
      
      . Id. at 27 (Figure 15), 294. The 27 percent national average was reported for Btu recovery of 94.2 percent. With Btu recovery at 90 percent the projected national average reduction by washing was 30 percent (with l'/2 inch top size and specific gravity at 1.6). Id. at 323.
     
      
      . Northern Appalachia was listed with an average reduction of 31 percent, id. at 12 (Figure 3), 267; the Eastern Midwest was listed with an average reduction of 30 percent, id. at 20 (Figure 9), 285; the Western Midwest was listed with an average reduction of 29 percent, id. at 23 (Figure 11), 292; 44 Fed.Reg. at 33593, col. 2.
     
      
      . Ad.Doc. No. II-A-90, supra note 232, at A-4, J.A. at 1222 (35 percent removal by washing assumed for coals with more than 2.5 lbs./MBtu). Ad.Doc. No. IV-E-11, supra note 240, at 1, J.A. at 3119 (35 percent removal by washing assumed for coals with more than 5.0 lbs./MBtu).
      The BOM data showed that reductions greater than the averages cited in n.296 supra could be attained when the sulfur content of the coal exceeded the average, and when the coal was crushed smaller than the l'A inch size, and/or the specific gravity of the float was less than 1.6. Late in the rulemaking EPA concluded that crushing to 3/s inch top size would be unduly expensive, lead to unacceptable energy loss, and pose coal handling problems. EPA found and NCA acknowledged that IV2 inch top size, 1.6 specific gravity represented common industiy practice. 44 Fed.Reg. at 33593, col. 2, & 33595, col. 3 — 33596, col. 1.
     
      
      . 44 Fed.Reg. at 33596, cols. 1-2; 45 Fed. Reg. at 8226, cols. 1-2.
      Recounting the evolution of the 27 percent figure puts petitioners’ challenge in perspective. Reassessment of the agency’s 35 percent coal washing assumption came in the context of the debate on whether the 1.2 lbs./MBtu emission limitation should be lowered. Following the September 1978 proposed NSPS the joint interagency working group investigated alternative standards lower than the proposed 1.2 lbs./MBtu ceiling. EPA stated that:
      the intent was to take full advantage of the cost effectiveness benefits of joint coal washing/scrubbing strategy on high-sulfur coal. The cost of washing is relatively inexpensive; therefore the group anticipated that a low emission ceiling, which would require coal washing and 90 percent scrubbing, could substantially reduce emissions in the East and Midwest at a relatively low cost. Since coal washing is now a widespread practice, it was thought that Eastern coal production would not be seriously impacted by the lower emission limit.
      44 Fed.Reg. at 33595, col. 3. At the December public hearing EPA received testimony on whether lower emission ceilings would preclude use of high sulfur coal reserves. One witness testified that if the degree of reduction achievable for coal washing was less than 35 percent assumed then the preclusion effect on high sulfur coal reserves would increase accordingly. Testimony of R. Ayres, Ad.Doc. No. IV-F-1, supra note 94, at 65, J.A. at 2970. Written comments expressed concern that a 35 percent reduction could not be achieved by coal washing on all high sulfur coal reserves. Ad. Doc. No. IV-D-756, supra note 242; Ad.Doc. No. IV-D-744, supra note 241, at 8-9, J.A. at 4734-35; Ad.Doc. No. IV-D-761, supra note 241; Ad.Doc. No. IV-D-848, supra note 241.
      In February 1978 EPA took a more detailed look at regional coal production impacts using the Bureau of Mines seam by seam data. The analysis identified the amount of reserves that would require more than 90 percent scrubbing of washed coal in order to meet the designated ceiling. To determine the potential sulfur reduction achievable through coal washing EPA assumed two levels of coal preparation technology which were thought to represent the state-of-the-art: crushing to l'A inch top size with separation at 1.6 specific gravity, and crushing to 3/s inch top size with 1.6 specific gravity.
      On April 5, 1979 a meeting was held in order for EPA and NCA to present their respective findings as they pertained to the potential impacts of lower emission standards on high-sulfur coal reserves in the Eastern Midwest and Appalachia and to discuss the degree of sulfur removal achievable with coal washing. As a result of this meeting EPA revised its assessment of state-of-the-art coal washing. EPA concluded that crushing to 3/s inch top size would be unduly expensive, lead to unacceptable energy loss, and pose coal handling problems. 44 Fed.Reg. at 33596, col. 1. EPA found and NCA acknowledged that IV2 inch top size and 1.6 specific gravity represented common industry practice. Id.
      
      On April 6, 1979 NCA submitted written documentation supplementing its concerns previously raised about the achievability of the 35 percent washing figure. Ad.Doc. No. IV-D-756, supra note 242. NCA stated “[b]ased on a review of the results currently being achieved using good engineering practice in operating mines, we believe that expectation (35 percent removal) to be optimistic by 5 to 10 percentage points.” Id. at 2, J.A. at 4778. This conclusion was based on limited data of actual coal practices under the former standards at a total of 46 mines in four states. The average actual reduction by washing in these states at the plants surveyed was, according to NCA, 27 percent. The average reduction in each of the four states ranged from 31 percent in Indiana, 27 percent in Illinois, 26 percent in West Virginia, to 20 percent in Ohio. These averages appear to have included washing figures for all coals including low and medium sulfur coals, which are more difficult to wash, although in these particular states there is a large proportion of high sulfur coal. However, as a consultant to the Electric Utilities stated, the data were not presented “in a manner suitable for a detailed analysis.” Brief for Petitioner APCO at B3.
      EDF’s written response vigorously objected to the pessimistic 27 percent average as being based on “a very select set of data from current operations... . ” Significantly, the 20 percent figure developed from Ohio was based on a survey of just 6.3 million tons of Ohio coal (from material provided by just two companies). This compares to a survey involving almost four times that amount of coal in Illinois —24.4 million tons. Ad.Doc. No. IV-D-763, supra note 243, at 3, J.A. at 4811. EDF pointed out that material already in the record supported the assumption that coal washing of high sulfur coal could achieve between 30 and 40 percent reduction. Id.
      
      With EPA’s announcement of the 90 percent standard it did not expressly maintain that it had retreated from the 35 percent assumption for washing high sulfur coal. Instead, it merely stated that IV2 inch top size and 1.6 specific gravity were present practice for coal washing. In the denial of the Electric Utilities’ petition for reconsideration EPA cited NCA’s data and indicated that 90 percent reduction requirement was attainable even if a coal washing plant achieved only the average 27 percent level of cleaning reported by NCA for conventional plants.
     
      
      . 44 Fed.Reg. at 33596, col. 1; Ad.Doc. No. IV-E-11, supra note 240, at 4, J.A. at 3122; Ad.Doc. No. IV-D-756, supra note 242, at 2, J.A. at 4777, 4778. The Electric Utilities stated that NCA “has submitted data to EPA demonstrating that the average sulfur removal that can be expected from coal cleaning is 25 to 30% (on a Btu basis).” Ad.Doc. No. IV-D-761, supra note 241, at 2, J.A. at 4834.
     
      
      . 45 Fed.Reg. at 8226, col. 1.
     
      
      . Brief for Petitioner APCO at B-3 (Memorandum from W. Pitts, for Entropy Environmentalists, Inc., to H. Nickel (July 3, 1980)).
     
      
      . Ad.Doc. No. III-B-3, supra note 9, at 4-10 to 4-11, J.A. at 1796-97 (“Process reliability is a minor problem.... ”). But see Brief for Petitioner APCO at 71 n.214, B-4; Reply Brief for Petitioner APCO at 15 & 17.
     
      
      . Portland Cement Ass’n v. Ruckelshaus, 486 F.2d 375, 396 (D.C.Cir.1973); Int'l Harvester Co. v. Ruckelshaus, 478 F.2d 615 (D.C.Cir.1973).
     
      
      . Ad.Doc. No. III-B-4, supra note 125, at 4-33 to 4-34, J.A. at 2343^4. See 40 CFR §§ 60.48a-49a, Appendix A (Method 19); 44 Fed.Reg. at 33618, col. 1 — 33619, col. 3.
     
      
      . Id.
      
     
      
      . Id.
      
     
      
      . Ad.Doc. No. Ill — B — 4, supra note 125, at 4-33 to 4-34, J.A. at 2343-44.
      Early in the rulemaking an EPA memorandum recommended that the credit:
      should be based on the actual anticipated cleaning for coal cleaning plants. If the burden of demonstrating compliance with the percent removal is placed on the utility [as the regulations do], the utility in turn will take measures (contractual) to assure and document that the cleaning plant performs as specified.
      Memorandum from T. Schrader to J. Farmer (EPA Nov. 9, 1977), Brief for Petitioner APCO at A-18.
     
      
      . Id. It also appears from the record that it would be possible for utilities to deal with unusually dirty coal by relying on coal blending with lower sulfur content coals. Or, since the regulations allow the utility to know ahead of time exactly what percentage of FGD must be achieved, the utility may rely on techniques for increasing FGD performance on the short term to take up the slack for low removal efficiency by coal washing. See n.271 supra.
      
     
      
      . The Electric Utilities’ argument that EPA never analyzed the national and regional impacts of FGD and coal washing combined in terms of environmental, energy, and cost considerations is without merit. E. g., 45 Fed.Reg. at 8223, cols. 2-3.
     
      
      . Ad.Doc. No. II-A-62, supra note 232. (This report cites two studies of the economics of combined PCC and FGD: L. Hoffman, “Engineering/Economic Analysis of Coal Preparation With S02 Cleanup Processes for Keeping High Sulfur Coals in the Energy Market” (BOM Contract No. J0155171); C. Miranda, “An Optimization Strategy for Control of SOX From Coal-Fired Power Plants”).
     
      
      . Electric Utility Steam Generating Units: Background Information for Proposed Particulate Matter Emission Standards, 3-12 to 3-13, J.A. 1301, 1352-54 (EPA Pub.No. 450/2-78-006a, July 1978) (Ad.Doc. No. III-B-1).
     
      
      . Id. at 3-13 to 3-14, Tables 3-7, 3-8, J.A. at 1353-54.
     
      
      . 40 C.F.R., Pt. 60, Subpart D (1976).
     
      
      . 44 Fed.Reg. at 33584, col. 1-2. The operation of baghouses and ESP’s was briefly described in National Lime Ass’n v. EPA, 627 F.2d 416, 424-25 (D.C.Cir.1980); and Portland Cement Ass’n v. Ruckelshaus, 486 F.2d 375, 390-91 (D.C.Cir.1973), cert. denied, 417 U.S. 921, 94 S.Ct. 2628, 41 L.Ed.2d 226 (1974).
     
      
      . Economic Evaluation of Fabric Filtration Versus Electrostatic Precipitation for Uitrahigh Particulate Collection Efficiency (EPRI) II — 5, J.A. 2737, 2765 (June 1978) (Ad.Doc. No. II — I— 388).
     
      
      . Ad.Doc. No. III-B-1, supra note 311, at 4-1 to 4-11, J.A. 1361-71.
     
      
      . Id.
      
     
      
      . Id.; Ad.Doc. No. II-I-388, supra note 315, at II — 5 to II — 6, J.A. at 2765-66.
     
      
      . Ad.Doc. No. III-B-1, supra note 311, at 4-6 to 4-7, J.A. at 1366-67; Ad.Doc. No. II-1-388, supra note 315; A. Walker, Characteristics and Electrostatic Collection of Particulate Emis
        
        sions From Combustion of Low Sulfur Western Coals 6, J.A. 2711, 2719 (June 1974) (Ad.Doc. No. II — I — 316).
     
      
      . Ad.Doc. No. III-B-1, supra note 319. Ad. Doc. No. II-I-388, supra note 315.
     
      
      . Id.; 44 Fed.Reg. at 33584, col. 3.
     
      
      . 43 Fed.Reg. at 42169, col. 2; Ad.Doc. No. II-I-388, supra note 315, at 11-20, J.A. at 2779.
     
      
      . Ad.Doc. No. III-B-1, supra note 311, at 4-11 to 4-13, J.A. at 1371-73.
     
      
      . Id. See Reigel & Bundy, Why the Swing to Baghouses, Power, January 1977, (referenced by EPA, Ad.Doc. No. III-B-1, supra note 311, at 4-13, 4-52, J.A. at 1373, 1412.)
     
      
      . Ad.Doc. No. Ill — B — I, supra note 311, at 4-16, J.A. at 1376.
     
      
      . Id. at 4-17, J.A. at 1377.
     
      
      . Id. at Appendix A, A-l, J.A. at 1471.
     
      
      . Id. at A-2, J.A. at 1472.
     
      
      . Id.
      
     
      
      . Id.
      
     
      
      . 44 Fed.Reg. at 33584, cols. 2-3; 43 Fed. Reg. at 42169, col. 2.
     
      
      . Ad.Doc. No. III-B-1, supra note 311, at A-2, J.A. at 1472.
     
      
      . Id.
      
     
      
      . 44 Fed.Reg. at 33584, col. 3.
     
      
      . Id. at 33584, col. 3-33585, col. 1.
     
      
      . 627 F.2d 416, 433 (D.C.Cir.1980). The standard of achievability described in National Lime represented a synthesis of prior decisions under the Clean Air Act. Id. at 452-53.
     
      
      . Ad.Doc. No. III-B-1, supra note 311, at 4-3 to 4-5, J.A. at 1363-65.
     
      
      . As in National Lime, no single defect in EPA’s ESP data base is so glaring that it alone would be fatal, but on a cumulative basis we could not uphold this standard if it hinged on the performance of ESP’s alone. 627 F.2d at 431-32. Of course, our decision to uphold the standard on the basis of EPA’s baghouse data does not mean that utilities are precluded from using ESP technology.
     
      
      . Lignite has been estimated to constitute approximately 20 percent of the nation’s coal reserves. Knust, Large Steam Generator Design As Inñuenced By Low Rank Coals (April 1968) (Ad.Doc. No. II-I-266). While it is true that no specific mention was made of lignite in the proposed and final rules, the Administrator explained in his denial of the petition for reconsideration that this was so because EPA had “extensively analyzed lignite-fired units in 1976 and concluded that they could employ the same types of control systems as those used for other coals.” 45 Fed.Reg. at 8229, col. 1 (citing Standards Support and Environmental Impact Statement Vol. I: Proposed Standards of Performance for Lignite-Fired Generators 11-29 referenced in Background Information for Proposed NOx Emission Standards at 9-13, J.A. 1505, 1679 (EPA Pub.No. 450/2-27-005a July 1978) (Ad.Doc. No. III-B-2)).
      However, EPA did consider relevant differences between lignite and other ranks of coal in establishing the revised NOx standard. There is a different NOx standard for lignite. 44 Fed. Reg. at 33587, col. 2.
      EPA’s denial of the petition for reconsideration does not expressly refer to, nor does it preclude, other materials on the record which appear to support the agency’s finding that lignite coals are no more difficult to control than some other coals. 45 Fed.Reg. at 8229, col. 1. See, e. g., Ad.Doc. No. II-I-388, supra note 315, at 1-2, 1-7, figures 1-1, 1-3, J.A. at 2750, 2755.
     
      
      . 43 Fed.Reg. at 42169, col. 2.
     
      
      . Ad.Doc. No. Ill — B — 1, supra note 311, at 4-3 to 4-5, J.A. at 1363-65.
     
      
      . Ad.Doc. No. II — I — 316, supra note 319, at 6, J.A. at 2719.
     
      
      . Ad.Doc. No. II — I — 316, supra note 319; Ad. Doc. No. Ill — I — 388, supra note 315.
     
      
      . Ad.Doc. No. Ill — B — 1, supra note 311, at 4-34 to 4-36, Table 4-2, J.A. at 1394-96.
     
      
      . Units 6, 8, 9, 11, 14, 17, 18, 19 and 20. EPA does not indicate what the design specifications were for the units tested.
     
      
      . Units 1, 2, 3, 4, 5, 7, 10, 12, 13, 15, 16 and 21.
     
      
      . Units 1, 2, 3, 4, 5, 6, 10, 12, 13, 14, 16 and 21.
     
      
      . Unit 6, .5 percent sulfur.
     
      
      . Id. at 4-38, Table 4-3, J.A. at 1398.
     
      
      . Units 2, 3, 6, 12, 13 and 21.
     
      
      . Units 1, 2, 3, 6, 10, 12, 13, 15, 17, 18 and 21.
     
      
      . Id. at 4-33, J.A. at 1393.
     
      
      . Unit 6, .5 percent sulfur.
     
      
      . 44 Fed.Reg. at 33584, col. 2; 43 Fed.Reg. at 42169, cols. 1-2.
      On the basis of EPA’s ESP data we are also at a loss to understand EPA’s statements concerning the size and temperature range that would be needed to meet the standard. See text at n. 331 supra. Giving EPA the benefit of doubt, these projected design features apparently are extrapolations from the test data. We are aware of formulas in the record for calculating the ESP specifications needed for achieving a given level of performance. See, e. g., Ad.Doc. No. III-B-1, supra note 311, at 4-4, J.A. at 1364. See also discussions of SCA sizing based on modified “Deutsch equation” at Ad.Doc. No. II — I — 388, supra note 315, at III — 10 to III — 13, J.A. 2814-17. However, EPA makes no attempt to explain or even reproduce its calculations. In fact, without careful and tedious scrutiny of the referenced data, a reader of the agency’s preamble would not know that an extrapolation has been made. Even after making this discovery we are expected to either accept the agency’s conclusions with a leap of faith or bridge the chasm between the technical data and the agency’s conclusions on our own. In this instance we decline to take either course.
     
      
      . E. g., “Five Field Performance Tests on Koppers Co. Precipitator,” Dust Collector Studies, John E. Amos Plant Unit No. 3, Appalachian Power Company, St. Albans, West Virginia, J.A. 2709-10 (title page and first page only) (Ad.Doc. No. II-I-296); “Report of Performance Acceptance Tests on the Cottrell Electrical Precipitation Equipment,” Virginia Electric Power Company, Mount Storm, West Virginia, Unit 2 (July 22, 1974) J.A. 4346-47 (title page and, page 3 only) (Ad.Doc. No. II-D-10); Memorandum from M. Davenport to S. Cuffe, “Trip Report — Centralia Generating Station, of Pacific Power and Light Company; Emission Source Tests, J.A. 4419 (EPA Aug. 16, 1977) (Ad.Doc. No. II-B-53).
     
      
      . See “References for Chapter 4,” Ad.Doc. No. III-B-1, supra note 311, at 4-53 to 4-54, J.A. 1413-14.
     
      
      . See note 184 supra.
      
     
      
      . It also appears that the test methods for acquiring the data base do not differ from the tests for compliance. See, e. g., 44 Fed.Reg. at 33608, col. 3-33609, col. 3.
     
      
      . Ad.Doc. No. II-I-388, supra note 315, at II — 5, J.A. at 2765.
     
      
      . Ad.Doc. No. II — I — 316, supra note 319, at ii, 10, J.A. at 2713, 2723.
     
      
      . Ad.Doc. No. II-I-388, supra note 315, at I — 1, J.A. at 2749.
     
      
      . Id. at V, J.A. at 2741.
     
      
      . 627 F.2d at 432-33.
     
      
      . 44 Fed.Reg. at 33584, col. 3-33585, col. 2.
     
      
      . Ad.Doc. No. III-B-1, supra note 311, at 4-16, J.A. at 1376.
     
      
      . Id., at 4-41, Table 4-5, J.A. at 1401.
     
      
      . Units 1, 2, 3 and 8.
     
      
      . Units 4, 5, 6 and 7.
     
      
      . Units 1, 2, and 3.
     
      
      . 44 Fed.Reg. at 33585, at col. 1.
     
      
      . Id. Ad.Doc. No. V-B-l, supra note 75, at 4-1, J.A. 2681 (Harrington Unit # 2 of Southwestern Public Service Co.).
     
      
      . 44 Fed.Reg. at 33585, col. 1.
     
      
      . Id.
      
     
      
      . Id.; 45 Fed.Reg. at 8227, cols. 1-2.
     
      
      . Brief for Petitioner APCO at 41, 76-77; Ad. Doc. No. IV-D-491a, supra note 186, at Appendix F, 12-13, J.A. at 3692-95; Ad. Doc. No. IV-D-611a, supra note 186, at 123-25, J.A. at 3847-49. Reply Brief for Petitioner APCO at 39.
     
      
      . 43 Fed.Reg. at 42169, col. 3; Ad. Doc. No. Ill — B — 1, supra note 308, at 4 — 13, J.A. at 1373.
     
      
      . 44 Fed.Reg. at 33585, col. 1.
     
      
      . The Electric Utilities noted these difficulties in their petition' for reconsideration. Operating Experience At Two Utility-Scale Bag-house Installations (GCA Corp.), Ad. Doc. No. VI-A-5, supra note 190, at Appendix E, 3 J.A. 5343, 5346 (July 1979).
     
      
      . 44 Fed.Reg. at 33585, col. 1; 45 Fed.Reg. at 8227, col. 2. Brief for Respondent EPA at 122.
     
      
      . Nebraska Public Power District’s Kramer Station, Stenby & Bye, The Kramer Baghouse, Combustion, October 1979, J.A. 5113 (Ad. Doc. No. VI-B-10).
     
      
      . Reply Brief of Petitioner APCO, at 41 n.l 12.
     
      
      . Ad. Doc. No. VI-B-10, supra note 380, at 35-36, J.A. at 5117-18.
     
      
      . Texas Utilities Generating Co.’s Monticello Station; Ad. Doc. No. VI-A- 5, supra note 190, at Appendix E at 6, J.A. at 5349.
     
      
      . Units 2 and 3. See Figure 24 in the appendix to this opinion.
     
      
      . Units 1, 4, 5, 6, 7 and 8 were industrial boilers. Units 1, 3, 4, 5, 6, and 7 were stoker-fired. Id.
      
     
      
      . Ad.Doc.No. Ill — B- 1, supra note 311, at 4-40, J.A. at 1400.
     
      
      . Ad.Doc. No. VI-A-5, supra note 190, Appendix E, J.A. at 5343. Brief for Petitioner APCO at 80.
     
      
      . See Ad.Doc. No. III — B — 1, supra note 311, at 8-3, Table 8-1, J.A. at 1445 (annualized cost of baghouses); Ad.Doc. No. II-A-64, supra note 232, at 3-12, Table 3-4, J.A. at 438 (operation and maintenance costs); Letter from L. Gibbs to W. Stevenson, J.A. 5379 (Nov. 19, 1979) (Ad.Doc. No. VI-B-12) (percent of operation and maintenance costs incurred for bag replacement).
     
      
      . See Brief for Respondent EPA at 124 n.92 (cost calculations).
     
      
      . 45 Fed.Reg. at 8227, col. 3.
     
      
      . Brief for Respondent EPA at 122-23, 125. These problems were recognized in the Electric Utilities’ Petition for Reconsideration. Ad.Doc. No. VI-B-5, supra note 190, at 3, 7, J.A. at 5346, 5350; and by EPA’s technical staff:
      The Harrington baghouse is not representative of the best system we recommend in our standards support document because all of the bags have been operated far beyond prudent engineering design limits. The bag-house is undersized for the application (3.5 to 1 A/C ratio v. our recommended 2.0 to 1). The underdesign error has been compounded by operating the baghouse at pressure drops (10-15 in H2O) far beyond proper design limits (5 in H20).
      It is not surprising that bag failures are a problem.
      Memorandum from J. Copeland to G. Crane J.A. 4715 (EPA Feb. 5, 1979) (Ad.Doc. No. IV — B — 29).
     
      
      . 45 Fed.Reg. at 8227, col. 3.
     
      
      . Id. at 8228, col. 1.
     
      
      . id.
      
     
      
      . National Lime Ass’n v. EPA, 627 F.2d 416, 433 (D.C.Cir.1980).
     
      
      . See 43 Fed.Reg. 42154 (Sept. 19, 1978).
     
      
      . 40 C.F.R. Subpart D § 60.43 (1976).
     
      
      . Like EDF, Sierra Club contends that the standard was based on political pressure, rather than EPA’s technical judgment. Brief for Petitioner Sierra Club at 70. Petitioner CARB stated that it “expects to support the position of the Environmental Defense Fund regarding ex parte communications between officials of the Environmental Protection Agency and private parties. CARB has not received a copy of EDF’s brief and must postpone its endorsement until it has reviewed the brief." Brief for Petitioner CARB at 5. However, in CARB’s subsequent reply brief it only supported and adopted by reference Sierra Club’s arguments regarding the variable standard.
     
      
      . Having raised this procedural attack on the rule in its motion for reconsideration, EDF is now properly before this court on the issue. 42 U.S.C. §§ 7607(d)(7)(B) & (8).
     
      
      . At times in its papers EDF appears to challenge the emission ceiling on the merits, implying that there is no support in the record for EPA’s decision to adopt the 1.2 lbs./MBtu ceiling. E. g., Brief for Petitioner EDF at 8-28. However, this approach is belied by EDF’s own characterization of its grounds for appeal as exclusively procedural, see Brief for Petitioner EDF at 10.
     
      
      . 43 Fed.Reg. at 42160, col. 2.
     
      
      . Id.
      
     
      
      . Under either option, midwestern coal production would increase to about 300 million tons, but without three monthly exemptions the use of reserves in some states would be restricted. “In the States of Ohio, Illinois, and in western Kentucky, 60 or more percent of reserves might be restricted even if coal cleaning were used.” Id.
      
     
      
      . Id. at cols. 2-3.
     
      
      . 44 Fed.Reg. at 33595, cols. 2-3.
     
      
      . Id. at col. 3.
     
      
      . 43 Fed.Reg. at 57835, cols. 1-3.
     
      
      . 44 Fed.Reg. at 33595 (citing results published in 43 Fed.Reg. at 57837-57859).
     
      
      . Draft Memorandum from J. Haines (Jan. 17, 1979) Appendix of Lodged Documents at B — 1.
     
      
      . Memorandum from D. Tundermann to B. Drayton, “NSPS Update” (Mar. 9, 1979), Appendix of Lodged Documents at B-3.
     
      
      . 44 Fed.Reg. at 33595, col. 3.
     
      
      . Id. at 33596, col. 1.
     
      
      . Id.
      
     
      
      . Id.
      
     
      
      . Id.
      
     
      
      . Id.
      
     
      
      . Id. at cols. 1-2.
     
      
      . Id. at col. 2.
     
      
      . Id.
      
     
      
      . Brief for Petitioner EDF at 10-14.
     
      
      . Id. at 14.
     
      
      . Memorandum from W. Barber to Files (undated) (Ad.Doc. No. IV-E-16). See Ackerman & Hassler, supra note 8, at 1549.
     
      
      . The parties have not made this task an easy one.
     
      
      . On April 29, 1979 Walter Barber of EPA spoke with Carl Bagge of NCA, to clarify the data submitted by NCA on April 6, 20, and 23, 1979. “The discussion focused on the effects of various assumptions on burnable coal reserves.” Memorandum from W. Barber to Files (May 1, 1979), J.A. at 4843 (Ad. Doc. No. IV-E-14) (referred to in Brief for Petitioner EDF at 16-17). Although it is not apparent from EDF’s brief, NCA made representations at the April 5 meeting about the regional coal dislocations NCA projected from promulgation of the proposed .55 standard. Other parties present asked NCA to back up its representations with data. It appears that the April 6, 20, and 23 submissions were NCA’s responses to the demand for support for its position at the April 5 meeting.
     
      
      . See text at nn. 487-90 infra.
      
     
      
      . Brief for Petitioner EDF at 35.
     
      
      . Id.
      
     
      
      . On March 28, 1979, a meeting was held among EPA staff, high level federal officials, and Senators from eastern coal states. EPA now indicates that the meeting did not concern the NSPS, and that after promulgation EPA erroneously reported the meeting in response to EDF’s FOIA request.
     
      
      . Memorandum from W. Barber to File (May 24, 1979) (Briefing Materials for Mar. 14, 1979 attached) J.A. at 4977 (Ad.Doc. No. IV-E-20). Affidavit of W. Barber, filed June 25, 1980.
     
      
      . Memorandum from C. Warren to K. Braithwaite (May 9, 1979), Appendix of Lodged Documents at A-2.
     
      
      . Id.
      
     
      
      . See n.298 & text at nn.399-402 supra.
      
     
      
      . E. g., Ad.Doc. No. IV-E-57, supra note 239, J.A. at 4765; Ad.Doc. IV-E-10, supra note 239, J.A. at 4775.
     
      
      . Ad.Doc. No. IV-E-11, supra note 240, J.A. at 3119; Ad.Doc. No. IV-E-12, supra note 240, J.A. at 4787 & J.A. at 5471-539.
     
      
      . Ad.Doc. No. IV-D-756, supra note 242, J.A. at 4777 (April 6, 1979); Letter from C. Bagge, for NCA, to D. Costle, J.A. at 4821 (April 20, 1979) (Ad.Doc. No. IV-D-760); Letter from C. Bagge, for NCA, to D. Costle, J.A. at 4827 (April 23, 1979) (Ad.Doc. No. IV-D-793); Ad.Doc. No. IV-E-14, supra note 410, J.A. at 4843 (April 29, 1979).
     
      
      . Memorandum from D. Hawkins to File, J.A. at 4839 (April 26, 1979) (Docketed May 1, 1979) (Ad.Doc. No. IV-3-13).
     
      
      . Id. The summary reads:
      The National Coal Association (NCA) representatives distributed materials sent to EPA on April 6, 20, and 23 alledging [sic] that adoption of an emissions ceiling more stringent than 1.2 pounds per million Btu would preclude substantially [sic] coal reserves in the east and midwest. Douglas Costle informed the participants at the meeting that it was not the Agency’s intent to rule out large portions of eastern or midwestem coal reserves as a result of setting the power plant new source performance standard. Stu Eizenstat confirmed that this was not the Administration’s intent either. Mr. Costle advised the NCA representatives that the material would be fully considered. Senator Byrd expressed his opinion that a decision to set an emission ceiling which would preclude the use of coal reserves would cause him great concern.
      As the April 23 letter from NCA does not indicate that copies have been provided to other major parties in the rulemaking, I am providing copies of that letter this day to the Utility Air Regulatory Group, NRDC, EDF and the Sierra Club.
     
      
      . 45 Fed.Reg. at 8215, col. 1.
     
      
      . “Briefing on Dry Scrubbing Technology,” Memorandum from J. Haines to Files, J.A. at 4851 (May 1, 1979) (Ad.Doc. No. IV-E-15); Affidavit of W. Barker, filed June 25, 1980.
     
      
      . Id.
      
     
      
      . Affidavit of D. Hawkins, filed August 25, 1980.
     
      
      . D. Hawkins’ Calendar, Appendix of Lodged Documents at A-5.
     
      
      . “Meeting on Coal-Fired Power Plants on April 30, 1979,” Memorandum from D. Hawkins to Files, J.A. at 4918 (attached to Ad.Doc. No. IV-E-24); Affidavit of D. Hawkins, filed June 25, 1980.
     
      
      . “Meeting to Discuss NSPS for Power Plants,” Memorandum from W. Barber to Files, J.A. at 4993 (May 24, 1979) (Ad. Doc. No. IV-E-21), Affidavit of D. Hawkins, filed Aug. 25, 1980.
     
      
      . Id.
      
     
      
      . Affidavit of D. Hawkins, filed Aug. 25, 1980.
     
      
      . Id.
      
     
      
      . Memorandum from D. Hawkins to W. Barber, J.A. at 4909 (dated May 8, 1979, docketed June 1, 1979) (Ad. Doc. No. IV-E-24).
     
      
      . The summary reads:
      The meeting was for the purpose of sharing our assessment of the Bureau of Mines’ information and National Coal Association’s information on coal reserves with Senator Byrd and to describe EPA’s own emission ceilings which were under consideration. The attached materials were supplied to the attendees of the meeting.
      
        Id.
      
     
      
      . In addition to reviewing EDF’s main procedural challenge to the 1.2 lbs./MBtu emission ceiling, we must also dispose of two pending motions involved in that challenge: (1) EDF’s Motion to Supplement the Record, filed May 14, 1980 (Civ. No. 79-1565), and (2) EDF’s Motion for Leave to Obtain Discovery, filed April 24, 1980 (Civ. No. 79-1565).
      1. EDF’s Motion to Supplement the Record
      
      EDF seeks to include in the rulemaking record provided for in 42 U.S.C. § 7607 several documents it contends support its challenge. These documents fall into five categories:
      (1) Documents which, according to EDF, evidence numerous ex parte contacts between EPA and interested parties either directly or through members of Congress or high level administration officials. Petitioner EDF’s Appendix of Lodged Documents, filed September 12, 1980, Schedule A.
      (2) Documents described by EDF as internal EPA communications which reflect the effect of the improper ex parte contacts on the evolution of the promulgated regulation. Id., Schedule B.
      (3) Documents which reflect EPA policies and Department of Justice advice regarding ex parte contacts. Id., Schedule C.
      (4) Documents relating to the use of adipic acid to improve scrubber efficiency, which EDF would have entered on the record had it “been given the opportunity to do so,” to refute the allegedly improper communications with EPA. Two out of the three documents in this category are studies already entered on the record at EDF’s request. The third document in this category is a letter from the Administrator responding to a Congressman’s request for information, which according to EDF, demonstrates that EPA considered and agreed with the results of the adipic acid studies, rather than, as EPA claims, considered and rejected the two studies. Id., Schedule D.
      (5) Any materials EDF acquires if this court grants EDF’s motion for further discovery. See infra.
      
      Except for the materials which are the subject of EDF’s discovery motion, all of the documents in question were obtained by EDF after the promulgation of the final standard as part of material released to EDF pursuant to a Freedom of Information Act request filed June 5, 1979. On April 2, 1980, EDF requested that EPA add the documents to the administrative record; the agency refused to do so on May 1, 1980. After EDF filed the instant motion, both EDF and EPA urged the court to defer its ruling until consideration of the merits of the review petition, and in the meantime to lodge the documents with the court. This request was granted. Order of June 16, 1980. Consequently, on September 12, 1980, the documents were lodged in a separate appendix, available to the court during the review.
      Our ruling now on supplementing the rule-making record with these documents in categories (l)-(4) is guided by the resolution of a similar controversy in Lead Industries Ass’n v. EPA, 647 F.2d 1130, at 1180-1181, 1184 (D.C.Cir.1980), cert. denied, 449 U.S. 1042, 101 S.Ct. 621, 66 L.Ed.2d 503 (1980). Both EPA and EDF agree that here, as in Lead Industries, which also involved a procedural challenge to the integrity of the rulemaking, a satisfactory solution is to lodge the documents with the court for the purpose of its review of the merits of EDF’s procedural arguments. Cf. American Petroleum Institute v. Costle, 609 F.2d 20, 22 (D.C.Cir.1979). Reply Brief for Petitioner EDF, at 32-33; Brief for Respondent EPA at 178. Since these documents have already been lodged and examined by us during our review of EDF’s procedural claims, there is no need formally to add them now to the rulemaking record, the contours of which are strictly defined in section 307, 42 U.S.C. § 7607. Hence the motion to formally add them to the rulemaking record is denied.
      2. EDF’s Motion for Leave to Obtain Discovery
      
      EDF seeks to take depositions from, or in the alternative to serve interrogatories on, five EPA officials, none of whom still occupy the offices they held at the time the motion was filed: Administrator Costie; Barbara Blum, Deputy Administrator; David Hawkins, Assistant Administrator for Air, Noise & Radiation; Charles Warren, Regional Administrator for Region II and former Director, Office of Legislation; and Walter Barber, Office of Air Quality Planning Standards. According to EDF the inquiries will be limited to “(1) the identity of participants in post-comment period conversations and meetings with private parties, members of Congress, and senior officials of other government agencies and offices; and (2) simple narrative descriptions of conversations and meetings, particularly by non-EPA participants.” EDF Motion, filed April 11, 1980, at 2.
      We find it neither necessary nor appropriate to permit discovery to supplement the extensive record already compiled in this case. Under the Clean Air Act, judicial review of NSPS is to be conducted — except in the most unusual circumstances — on the record provided for in the Act. Section 307(d)(7)(A), 42 U.S.C. § 7607(d)(7)(A). In contrast to instances where agency decisionmakers may be required to submit affidavits or to testify because no explanation for agency action appears on the record, see Citizens to Preserve Overton Park, Inc. v. Volpe, 401 U.S. 402, 420, 91 S.Ct. 814, 825, 28 L.Ed.2d 136 (1971), this is a case where EPA has, in keeping with the explicit procedures required by the Clean Air Act, submitted a substantial explanation for its promulgation of the standard and its denial of the petition for reconsideration. These statements and the underlying record must therefore serve as the basis for our review. See Camp v. Pitts, 411 U.S. 138, 143, 93 S.Ct. 1241, 1244, 36 L.Ed.2d 106 (1973).
      We are aware that in certain circumstances, in order to afford effective review, it may be necessary for the court to order affidavits and other evidence to be submitted directly to it. See National Nutritional Foods Ass’n v. FDA, 491 F.2d 1141, 1144 (2d Cir.), cert. denied, 419 U.S. 874, 95 S.Ct. 135, 42 L.Ed.2d 113 (1974); see also Home Box Office, Inc. v. FCC, 567 F.2d 9, 52 (D.C.Cir.), cert. denied, 434 U.S. 829, 98 S.Ct. 111, 54 L.Ed.2d 89 (1977) (court sua sponte ordered the Commission to provide “a list of all of the ex parte presentations, together with the details of each, made to it, or any of its members or representatives, during the rule-making proceedings”). Cf. 42 U.S.C. § 7607(c) (court may require EPA to take additional evidence). In this case, however, the court has already required, and EPA has filed, affidavits concerning post-comment period meetings. We do not now discern any serious gaps in the record which frustrate our ability to appraise EDF’s procedural challenges. The record already contains much, if not all, of the information that EDF desires: i. e., “what meetings took place, who attended, what information was imparted, and what use was made of the material.” Brief for Petitioner EDF at 83.
      Although further discovery might be warranted upon a “strong showing of bad faith or improper behavior,” see Citizens to Preserve Overton Park, Inc. v. Volpe, supra, 401 U.S. at 420, 91 S.Ct. at 825, it follows from our discussion below on the merits of EDF’s appeal, that it has not made the requisite showing of bad faith or improper conduct which would create serious doubts about the fundamental integrity of this rulemaking proceeding. For these reasons the motion for additional discovery is denied.
     
      
      . See Affidavits of W. Barber and D. Hawkins, filed June 25, 1980.
     
      
      . Brief for Petitioner EDF at 44.
     
      
      . Affidavit of D. Hawkins filed Aug. 25, 1980.
     
      
      . Brief for Petitioner EDF at 36.
     
      
      . Congress has defined “ex parte communication[s]” in formal rulemaking and adjudication proceedings as “oral or written- communication[s] not on the public record with respect to which reasonable prior notice to all parties is not given . . . .” 5 U.S.C. § 551(14) (emphasis supplied). We do not believe that it is useful to use the same term also to describe communications in an informal rulemaking context which are docketed on the public record. See n.501 and accompanying text, infra.
      
     
      
      . 42 U.S.C. § 7607(d)(9)(D).
     
      
      . 42 U.S.C. § 7607(d)(8).
     
      
      . 435 U.S. 519, 98 S.Ct. 1197, 55 L.Ed.2d 460 (1978). See generally Stewart, Vermont Yankee and the Evolution of Administrative Procedure, 91 Harv.L.Rev. 1804 (1978); Byse, Vermont Yankee and the Evolution of Administrative Procedure: A Somewhat Different View, 91 Harv.L.Rev. 1823 (1978); Scalia, Vermont Yankee: The APA, the D.C. Circuit, and the Supreme Court, 1978 Sup.Ct.Rev. 345.
     
      
      . 435 U.S. at 523-25, 542-49, 98 S.Ct. at 1201-1202, 1210-1214.
     
      
      . Id. at 524, 98 S.Ct. at 1202.
     
      
      . Id. at 549, 98 S.Ct. at 1214. See Lead Industries Ass’n v. EPA, 647 F.2d 1130, at 1169 (D.C.Cir.1980), cert. denied, 449 U.S. 1042, 101 S.Ct. 621, 66 L.Ed.2d 503 (1980) (“the Supreme Court’s decision in the Vermont Yankee case makes it absolutely clear that the court must be extremely reticent about going beyond the procedures established by Congress and requiring agencies to provide additional procedures in rulemaking proceedings.”).
     
      
      . “As a general rule, due process probably imposes no constraints on informal rulemaking beyond those imposed by statute. See Willapoint Oysters, Inc. v. Ewing, 174 F.2d 676, 694 (9th Cir. 1949) [cert. denied, 338 U.S. 860, 70 S.Ct. 101, 94 L.Ed. 527 (1949)].” United Steelworkers of America v. Marshall, 647 F.2d 1189 at 1215 n.28 (D.C.Cir.1980) (declining to extend Home Box Office ex parte limitations to intraagency contacts in OSHA informal rulemaking proceedings). Cf. Due Process and Ex Parte Contacts in Informal Rulemaking, 89 Yale L.J. 194 (1979) (arguing due process requires that all ex parte contacts during comment period be banned, and any subsequent contacts be put in public record).
     
      
      . 42 U.S.C. § 7607(d)(8), (d)(9)(D).
     
      
      . That section states, in part:
      (2) Not later than the date of proposal of any action to which this subsection applies, the Administrator shall establish a rulemaking docket for such action (hereinafter in this subsection referred to as a “rule”). Whenever a rule applies only within a particular State, a second (identical) docket shall be simultaneously established in the appropriate regional office of the Environmental Protection Agency.
      (3) In the case of any rule to which this subsection applies, notice of proposed rule-making shall be published in the Federal Register, as provided under section 553(b) of Title 5, shall be accompanied by a statement of its basis and purpose and shall specify the period available for public comment (hereinafter referred to as the “comment period”). The notice of proposed rulemaking shall also state the docket number, the location or locations of the docket, and the times it will be open to public inspection. The statement of basis and purpose shall include a summary of—
      (A) the factual data on which the proposed rule is based;
      (B) the methodology used in obtaining the data and in analyzing the data; and (C) the major legal interpretations and policy considerations underlying the proposed rule.
      The statement shall also set forth or summarize and provide a reference to any pertinent findings, recommendations, and comments by the Scientific Review Committee established under section 7409(d) of this title and the National Academy of Sciences, and, if the proposal differs in any important respect from any of these recommendations, an explanation of the reasons for such differences. All data, information, and documents referred to in this paragraph on which the proposed rule relies shall be included in the docket on the date of publication of the proposed rule.
      (4) (A) The rulemaking docket required under paragraph (2) shall be open for inspection by the public at reasonable times specified in the notice of proposed rulemaking. Any person may copy documents contained in the docket. The Administrator shall provide copying facilities which may be used at the expense of the person seeking copies, but the Administrator may waive or reduce such expenses in such instances as the public interest requires. Any person may request copies by mail if the person pays the expenses, including personnel costs to do the copying.
      (B)(i) Promptly upon receipt by the agency, all written comments and documentary information on the proposed rule received from any person for inclusion in the docket during the comment period shall be placed in the docket. The transcript of public hearings, if any, on the proposed rule shall also be included in the docket promptly upon receipt from the person who transcribed such hearings. All documents which become available after the proposed rule has been published and which the Administrator determines are of central relevance to the rulemaking shall be placed in the docket as soon as possible after their availability.
      (ii) The drafts of proposed rules submitted by the Administrator to the Office of Management and Budget for any interagency review process prior to proposal of any such rule, all documents accompanying such drafts, and all written comments thereon by other agencies and all written responses to such written comments by the Administrator shall be placed in the docket no later than the date of proposal of the rule. The drafts of the final rule submitted for such review process prior to promulgation and all such written comments thereon, all documents accompanying such drafts, and written responses thereto shall be placed in the docket no later than the date of promulgation.
      (5) In promulgating a rule to which this subsection applies (i) the Administrator shall allow any person to submit written comments, data, or documentary information; (ii) the Administrator shall give interested persons an opportunity for the oral presentation of data, views, or arguments, in addition to an opportunity to make written submissions; (iii) a transcript shall be kept of any oral presentation; and (iv) the Administrator shall keep the record of such proceeding open for thirty days after completion of the proceeding to provide an opportunity for submission of rebuttal and supplementary information.
      (6) (A) The promulgated rule shall be accompanied by (i) a statement of basis and purpose like that referred to in paragraph (3) with respect to a proposed rule and (ii) an explanation of the reasons for any major changes in the promulgated rule from the proposed rule.
      (B) The promulgated rule shall also be accompanied by a response to each of the significant comments, criticisms, and new data submitted in written or oral presentations during the comment period.
      (C) The promulgated rule may not be based (in part or whole) on any information or data which has not been placed in the docket as of the date of such promulgation.
      (7) (A) The record for judicial review shall consist exclusively of the material referred to in paragraph (3), clause (i) of paragraph (4)(B), and subparagraphs (A) and (B) of paragraph (6).
      (B) Only an objection to a rule or procedure which was raised with reasonable specificity during the period for public comment (including any public hearing) may be raised during judicial review. If the person raising an objection can demonstrate to the Administrator that it was impracticable to raise such objection within such time or if the grounds for such objection arose after the period for public comment (but within the time specified for judicial review) and if such objection is of central relevance to the outcome of the rule, the Administrator shall convene a proceeding for reconsideration of the rule and provide the same procedural rights as would have been afforded had the information been available at the time the rule was proposed. If the Administrator refuses to convene such a proceeding, such person may seek review of such refusal in the United States court of appeals for the appropriate circuit (as provided in subsection (b) of this section. Such reconsideration shall not postpone the effectiveness of the rule. The effectiveness of the rule may be stayed during such reconsideration, however, by the Administrator or the court for a period not to exceed three months.
      (8) The sole forum for challenging procedural determinations made by the Administrator under this subsection shall be in the United States court of appeals for the appropriate circuit (as provided in subsection (b) of this section) at the time of the substantive review of the rule. No interlocutory appeals shall be permitted with respect to such procedural determinations. In reviewing alleged procedural errors, the court may invalidate the rule only if the errors were so serious and related to matters of such central relevance to the rule that there is a substantial likelihood that the rule would have been significantly changed if such errors had not been made.
      (9) In the case of review of any action of the Administrator to which this subsection applies, the court may reverse any such action found to be—
      (A) arbitrary, capricious, an abuse of discretion, or otherwise not in accordance with law;
      (B) contrary to constitutional right, power, privilege, or immunity;
      (C) in excess of statutory jurisdiction, authority, or limitations, or short of statutory right; or
      (D) without observance of procedure required by law, or (i) such failure to observe such procedure is arbitrary or capricious, (ii) the requirement of paragraph (7)(B) has been met, and (iii) the condition of the last sentence. of paragraph (8) is met.
      42 U.S.C. § 7607(d).
     
      
      . Id. at 319, 4 L.H. 2786.
     
      
      . Pedersen, Formal Records and Informal Rulemaking, 85 Yale L.J. 38, 78 (1975).
     
      
      . Id. at 64.
     
      
      . This approach was advocated in a 1975 recommendation by The Administrative Conference of the United States (“ACUS”), which proposed that factual information “that was considered by the authority responsible for promulgation of the rules” be included in an informal rulemaking record. Recommendation No. 74-4, Preenforcement Judicial Review of Rules of General Applicability, 1 C.F.R. § 305.74-4(1)(4) (1975).
     
      
      . Pedersen, supra note 467, at 72, 80.
     
      
      . 313 U.S. 409, 422, 61 S.Ct. 999, 1004, 85 L.Ed. 1429 (1941) (“Morgan IV”); Morgan v. United States, 304 U.S. 1, 18, 58 S.Ct. 773, 776, 82 L.Ed. 1129 (1938) (“Morgan II”).
      
     
      
      . Pedersen, supra note 467, at 78-79. Among Pedersen’s specific proposals were the following:
      [A]ll public comments received during the comment period and all transcripts of hearings held concerning the proposal would likewise be placed in the comment file upon receipt by the agency. ... All documents which became available after the proposal had been published and which the agency decided were of central relevance to the rule-making would likewise be placed in the file. If the documents were important enough, the present requirement of Portland Cement [486 F.2d 375 (D.C.Cir.1973), cert. denied, 417 U.S. 921, 94 S.Ct. 2628, 41 L.Ed.2d 226 (1974)] might call for an extension of the comment period, or even for the proposal of an amended rule.
      [T]he final rule, with its support documents, would close the file. The contents of the file would be the exclusive record for judicial review. Nothing that had not properly been placed in the file would be considered by the court.
      
      Pedersen, supra note 467, at 79 (emphasis partially supplied).
     
      
      . 42 U.S.C. § 7607(d)(6)(C), (d)(7)(A).
     
      
      . See 42 U.S.C. § 7607(d)(3)-(7).
     
      
      . The FTC at one time prohibited all ex parte contacts between outside persons and Commissioners or staff assistants during a rulemaking. 42 Fed.Reg. at 43973-74 (1977). FTC ex parte limitations are now governed by statute. P.L. 96-252, 94 Stat. at 379-80 (May 28, 1980) (provided that all ex parte communications with specified FTC officials be made public). In discussing the ex parte restriction, a Senate report explicitly stated that
      By recommending adoption of special requirements for disclosure of ex parte communications between the rulemaking staff and the [Federal Trade] Commission ..., the Committee does not endorse any general departure from the long established requirements in rulemaking proceedings of other agencies. The Committee acknowledges the concern that, in other agency rulemaking proceedings, such requirements could unduly rigidify the decision process and unduly hamper internal communication, but the Committee recommends the application of disclosure requirements here because it feels that such requirements will not unduly hamper or rigidify [these] rulemakings.
      S.Rep. No. 96-184 at 22 n.7 (1979) (emphasis supplied). See also 47 C.F.R. § 1 (1979) (FCC rules); 14 C.F.R. § 300.2 (1979) (CAB rules); 16 C.F.R. § 1012 (1979) (CPSC rules).
     
      
      . 42 U.S.C. § 7607(d)(4)(B)(i).
     
      
      . See Certified List of the Contents of the Record, at Category IV-D, pp. 41-63. EDF gives us no reason to believe EPA was guilty of bad faith or deception in failing to place all materially relevant written submissions into the docket. Cf. Brief for Respondent EPA, at 135-36.
     
      
      . Cf. United Air Lines, Inc. v. CAB, 309 F.2d 238, 241 (D.C.Cir.1962) (holding that ex parte communications in an adjudicatory proceeding did not invalidate CAB’s award of a certificate because, inter alia, those communications “were placed in a public file”). We agree with Professor Davis’ remark that, as a general matter, “[i]f placing the communications in the public file is enough even in an adjudication, it should be enough in rulemaking.” I K. Davis, Administrative Law Treatise § 6:18 at 535 (2d ed. 1978).
     
      
      . 42 U.S.C. § 7607(d)(7)(B) (emphasis supplied).
     
      
      . EPA Decision in Response to Petitions for Reconsideration, 45 Fed.Reg. at 8214, col. 3.
     
      
      . 42 U.S.C. § 7607(d)(9)(D).
     
      
      . 42 U.S.C. § 7607(d)(8).
     
      
      . See 42 U.S.C. § 7607(d)(4)(B)(i), and discussion immediately infra.
      
     
      
      . 42 U.S.C. § 7607(d)(4)(B)(i).
      In general, factual or methodological information which is critical to a proposed rule should be available in such a way as to provide an adequate opportunity for comment. See, e. g., Portland Cement Ass'n v. Ruckelshaus, 486 F.2d 375, 394, 402 (D.C.Cir.1973), cert. denied, 417 U.S. 921, 94 S.Ct. 2628, 41 L.Ed.2d 226 (1974). See also Home Box Office, Inc. v. FCC, 567 F.2d 9, 55 (D.C.Cir.), cert. denied, 434 U.S. 829, 98 S.Ct. 111, 54 L.Ed.2d 89 (1977) (stressing importance of “adversarial comment”); United States v. Nova Scotia Food Products Corp., 568 F.2d 240, 252 (2d Cir. 1977) (criticizing FDA’s failure to put scientific data on the record); Int'l Harvester Co. v. Ruckelshaus, 478 F.2d 615, 631-32 (D.C.Cir.1973) (criticizing EPA’s failure to provide opportunity to comment on methodology used in investigations concerning its decision not to suspend application of new auto emission standards). But cf. FCC v. WNCN Listeners Guild, 450 U.S. 582, 591, 101 S.Ct. 1266, 1272 n.22, 67 L.Ed.2d 521 (1981), rev'g and remanding, 610 F.2d 838, 846-47 & n.24 (D.C.Cir.1979) (en banc) (Although Commission failed to disclose “important” staff study prior to issuing formal policy statement, thereby depriving participants of opportunity to comment upon the study, Court holds that “the action of the Commission, even if a procedural lapse, [was not] a sufficient ground for reopening the proceedings before the Commission”).
     
      
      . See generally Verkuil, Jawboning Administrative Agencies: Ex Parte Contacts by the White House, 80 Colum.L.Rev. 943, 988 n.233 (1980).
     
      
      . See generally W. Gellhom, C. Byse & P. Strauss, Administrative Law 854 (7th ed. 1979) (“the administrator must answer to the world of politics — to the legislature, the executive, the press, the trade association, the consumer group — as well as to the judiciary, and this supposes meetings, pressures, and demands few judges encounter”).
      We note that during the spring of 1979 the trade journals carried reports of the serious consideration being given to a ceiling lower than 1.2 lbs./MBtu; of the possibility of a combined washing-scrubbing basis for the 90 percent reduction standard; of the refusal of utilities to buy coal they would have to scrub more than 90 percent; and of the Byrd meeting with the Administrator. In their recent book, Ackerman and Hassler summed it up thus: a “reader of the weekly BNA Environmental Re
        
        porter would have no difficulty following the main course of the decision. ...” See Ackerman & Hassler, supra note 8, at 113; see also Banks, supra note 8, at 67 (account of the press coverage during the pre-publication period).
     
      
      . See, e. g„ Ethyl Corp. v. EPA, 541 F.2d 1, 48-53 (D.C.Cir.) (en banc), cert. denied, 426 U.S. 941, 96 S.Ct. 2662, 49 L.Ed.2d 394 (1976) (in addition to extending the comment period, EPA also admitted studies and comments after the extended period had closed). EPA states in its brief that it has a “long-standing general practice of accepting late comment[s].” Brief for Respondent EPA, at 135. See, e. g., Environmental Defense Fund, Inc. v. Blum, 458 F.Supp. 650, 654 (D.D.C.1978).
     
      
      . See 42 U.S.C. § 7411(b)(6).
     
      
      . See Sierra Club v. Costle, Civ. Action No. 78-1297 (D.D.C. July 25, 1978).
     
      
      . See Ad.Doc. No. IV-J-25.
     
      
      . H.Rep. No. 95-294, supra note 47, at 319, U.S.Code Cong. & Admin.News at 1398, 4 L.H. 2786. See 42 U.S.C. § 7607(d)(4), (d)(5); cf. n.484 supra.
      
     
      
      . 42 U.S.C. § 7607(d)(7)(B).
     
      
      . Our own analysis of the communications between EPA and outside sources during the post-comment period persuades us, furthermore, that the agency was not victimized by any “ex parte blitz” from coal and utility industry advocates; rather, all sides attempted to keep in touch with EPA and make their positions known — both orally and in writing — right up until promulgation of the final rule.
     
      
      . See nn.296-97, and text at nn.298-99, supra.
      
     
      
      . Brief for Petitioner EDF at 16; see Ad.Doc. No. IV-E-11, supra note 240, J.A. at 3119.
     
      
      . Ad.Doc. No. IV-D-763, supra note 243, J.A. at 4809.
     
      
      . EDF had an additional period of almost eight months between June, 1979 and February, 1980 during which its petition for reconsideration was pending, to provide additional rebuttal material. During this time the Electronic Utilities analyzed NCA’s data and concluded that it was basically consistent with the record. See nn.298, 301 supra.
      
      With regard to EPA’s own analysis conducted in February 1979 on the availability of coal reserves, EDF states “[t]here is no recorded evidence of the ‘new EPA analysis,’ nor has the public been offered an opportunity to comment upon them.” Reply Brief for Petitioner EDF at 7-8. This statement is contrary to EDF’s admission that it received copies of EPA’s reserve analysis at the April 5 meeting. Brief for Petitioner EDF at 15. Moreover, the statement is incorrect. EPA’s analysis was distributed and docketed before the April 5 meeting, Ad.Doc. No. IV-B-57, supra note 239, distributed at the April 5 meeting attended by EDF, Ad.Doc. No. IV-E-11, supra note 440, and docketed again after the meeting, Ad.Doc. No. IV-E-12, supra note 240. The BOM coal data underlying EPA’s analysis was published in 1976 and dis-
      cussed throughout the rulemaking. EDF could have obtained this data, as the court did, from the library of the Department of the Interior.
      EDF claims that remand is necessary to afford it the opportunity to examine “scrubber efficiency,” “the increased efficiency of scrubbers using adipic acid,” “the fundamental flaw in confusing production with reserves,” and “the greatly reduced S02 emissions which would result from required coal washing.” Reply Brief for Petitioner EDF at 27. But these subjects were fully considered and debated throughout the rulemaking. For example, EDF cites two studies on the use of adipic acid to increase scrubber efficiency which it claims refute the need to retain the 1.2 lbs./MBtu ceiling. Brief for Petitioner EDF at 50-52. These studies were available in December and March, 1979 and EPA entered them into the record at EDF’s request on June 3, 1980. EPA discussed the use of adipic acid in its denial of EDF’s petition for reconsideration. 45 Fed. Reg. at 8212, col. 3. But more importantly, the subject of additives such as adipic acid and their effect on scrubber efficiency was well known to EPA from the outset of the rulemaking. During the public comment period EDF did, in fact, submit written comments and testimony which brought the subject of adipic acid to the agency’s attention. See Ad.Doc. No. IV-D-631, supra note 203, at V-98, J.A. at 4707 (EDF comments); Ad.Doc. No. IV-F-1, supra note 94, at 189, J.A. at 3075 (testimony of R. Rauch for EDF). In sum, EDF’s contention that it was denied the opportunity to comment on adipic acid and other relevant subjects is without merit.
     
      
      . Compare Logansport Broadcasting Corp. v. United States, 210 F.2d 24, 28 (D.C.Cir.1954) (“Surely every time the Commission decided to take account of some additional factor it was not required to start the proceedings all over again. If such were the rule the proceedings might never be terminated”), with 42 U.S.C. § 7607(d)(7)(B) (EPA must reconsider its rule-making if an objection “arose after the period for public comment,” and it is “of central relevance to the outcome of the rule” (emphasis supplied)).
     
      
      . Sangamon Valley Television Corp. v. United States, 269 F.2d 221, 224 (D.C.Cir.1959) (FCC channel assignment proceeding involved claims of this sort, and “basic fairness requires such proceeding to be carried on in the open”).
     
      
      . See United States Lines, Inc. v. FMC, 584 F.2d 519, 539-40 (D.C.Cir.1978) (informal adjudication); cf. United Steelworkers of America v. Marshall, 647 F.2d 1189, at 1237-1238 (D.C.Cir.1980); Action for Children’s Television v. FCC, 564 F.2d 458, 474-77 (D.C.Cir,1977) (both cases distinguishing informal rulemaking from “valuable privilege” adjudications for purposes of ex parte limitations)'. See generally Verkuil, supra note 485, at 970-78.
     
      
      . See generally Verkuil, supra note 485, at 975-76:
      It should not be forgotten that informal rule-making involves “interested persons,” rather than “parties” in the usual adjudicative sense of the term. The concept of “ex parte” implies a different decisional structure from that involving mere “interested persons.” One can only have a contact without “parties” present in a proceeding where parties are involved, namely, adjudication or formal rulemaking.
      
        See also Verkuil, The Emerging Concept of Administrative Procedure, 78 Colum.L.Rev. 258, 290 (1978); Nathanson, Report to the Select Committee on Ex Parte Communications in Informal Rulemaking Proceedings, 30 Admin.L. Rev. 377, 396-97 (1978):
      In the ordinary rulemaking proceedings the parties are not identified in advance. Neither are conflicting interests established in advance among those subject to the proposed regulations.... In such a situation the very concept of ex parte communications is strikingly out of place; there are no parties to begin with, and it is not known what parties will develop and what their conflicting interests will be.
     
      
      . “Democratic ideology requires control of administrative action by elected representatives of the people.” Scher, Conditions for Legislative Control, 25 J. Politics 526 (1963). See Stewart, The Reformation of American Administrative Law, 88 Harv.L.Rev. 1669, 1672-73 (1975).
     
      
      . See Remarks of Carl McGowan (Chief Judge, U.S. Court of Appeals, D.C. Circuit), Ass’n of Amer. Law Schools, Section on Admin. Law (San Antonio, Texas, Jan. 4, 1981):
      I think it likely that ambivalence will continue to pervade the ex parte contact problem until we face up to the question of whether legislation by informal rulemaking under delegated authority is, in terms of process, to be assimilated to lawmaking by the Congress itself, or to the adversary trial carried on in the sanitized and insulated atmosphere of the courthouse. Anyone with experience of both knows that a courtroom differs markedly in style and tone from a legislative chamber. The customs, the traditions, the mores, if you please, of the processes of persuasion, are emphatically not the same. What is acceptable in the one is alien to the other.
      
        See generally Ex Parte Communication During Informal Rulemaking, 14 Colum. J. L. & Soc. Prob. 269, 275 (1979).
     
      
      . See K. Davis, supra note 478, § 6:19 at 537 (“Communications of all sorts are the life of a notice and comment proceeding. The more the better. They should not be prohibited. They should be invited and encouraged.”); W. Gellhorn, C. Byse & P. Strauss, supra note 486, at 871; Ackerman & Hassler, supra note 8, at 1563-64 (“the threat to agency learning is only one half of the price of undue formalism... . At present, EPA officials often meet with outsiders at both technical and policy-making levels, getting new ideas and informally gauging response to possible regulatory initiatives. A formalistic approach to ‘outside intervention’ would jeopardize this rich set of informal contacts, destroying a vital supplement to the inevitably inadequate publications in the Federal Registe!”). See generally American Airlines, Inc. v. CAB, 359 F.2d 624, 630 (D.C.Cir.), cert. denied, 385 U.S. 843, 87 S.Ct. 73, 17 L.Ed.2d 75 (1966) (“Rule making has a unique value and importance as an administrative technique for evolution of general policy, notwithstanding, or perhaps indeed because of, the freedom from the procedures carefully prescribed to assure fairness in individual adjudication.”); Strauss, Disqualifications of Decisional Officials in Rulemaking, 80 Colum.L.Rev. 990, 1049 (1980) (concluding that “neither acts nor beliefs producing the decision to initiate a rule, the formulation of a proposal, or the conduct of policy discussions with Congress, the regulated industry, or the public should be regarded as disqualifying” (emphasis supplied)).
     
      
      . Home Box Office, Inc. v. FCC, 567 F.2d 9, 54 (D.C.Cir.), cert. denied, 434 U.S. 829, 98 S.Ct. 111, 54 L.Ed.2d 89 (1977).
     
      
      . 42 U.S.C. § 7607(d)(6)(C).
     
      
      . Action for Children’s Television v. FCC, 564 F.2d 458, 474-75 n.28 (D.C.Cir.1977) (emphasis supplied).
      Congressional intent not to restrict ex parte contacts in informal rulemaking under the APA — an intent expressed just prior to enactment of the 1977 Clean Air Act Amendments— could not have been clearer. “Informal rule-making proceedings ... will not be affected by the [Sunshine Act] provision.” Senate Comm, on Gov’t Operations, Rept. to Accompany S. 5, Gov’t in the Sunshine Act, S.Rep. No. 94-354, 94th Cong., 1st Sess. 35 (1975). See also 121 Cong.Rec. 35330 (1975) (remarks of Sen. Kennedy) (“informal rulemaking proceedings are also susceptible to ex parte influence. These areas are, however, left untouched by the provisions of [the Sunshine Act]”).
     
      
      . 567 F.2d 9 (D.C.Cir.), cert. denied, 434 U.S. 829, 98 S.Ct. 111, 54 L.Ed.2d 89 (1977).
     
      
      . See cases cited at n.500 supra; K. Davis, supra note 478, at § 6:18.
     
      
      . This discussion immediately infra applies to oral communications generally. Disclosure of communications involving Executive Branch officials are specifically addressed in subpart (a) infra.
      
     
      
      . 42 U.S.C. § 7607(d)(6)(C).
     
      
      . Cf. Action for Children’s Television v. FCC, 564 F.2d 458, 475 n.28 (D.C.Cir.1977) (no blanket “logging” requirement under informal rule-making procedures of the APA, § 553).
      EDF believes that the statute, 42 U.S.C. § 7607(d)(4)(B), (d)(5), requires a transcript of any oral presentation in the course of the rule-making. See, e. g., Reply Brief for Petitioner EDF at 4. In context, however, we think the transcript requirement refers to formal presentations made on request during the comment period, and is designed to insure that both oral and written presentations made during that time are included in the record. It does not mean that a party can demand an opportunity for an oral presentation or insist upon a full transcript of such presentation being inserted in the record after the comment period has closed. We believe the Administrator may receive oral contacts thereafter without making a complete transcript of such contacts, however useful such recording might be to ward off criticism. All oral contacts, in other words, are not “oral presentation[s]” within the meaning of the statute.
     
      
      . 42 U.S.C. § 7607(d)(6)(C). EPA’s own internal procedures are consistent with this interpretation of the statute. EPA allows meetings with “interested persons” in the period between proposal and promulgation but “[i]n all cases, however, a written summary of the significant points made at the meetings must be placed in the comment file.” Memorandum from the Administrator, Ex Parte Contacts in EPA Rulemaking, App. of Lodged Documents, Schedule C-l (Aug. 4, 1977). This requirement applies “to every form of. discussion with outside interested persons,” in meetings or over the telephone, “as long as the discussion is significant.” “All new data or significant arguments presented at the meeting should be reflected in the memorandum.” Id.
      
      Many commentators agree that ex parte comments during informal rulemaking should not be restricted; but there is also agreement that at least those communications which produce significant new information should be noted on a public record. See, e. g., K. Davis, supra note 478, at § 6:18; 1 C.F.R. § 205.77-3 (1980) (Admin. Conf. of the United States, Ex Parte Communications in Informal Rulemaking Proceedings, Rec. No. 77-3):
      1. A general prohibition applicable to all agencies against the receipt of private oral or written communications is undesirable, because it would deprive agencies of the flexibility needed to fashion rulemaking procedures appropriate to the issues involved, and would introduce a degree of formality that would, at least in most instances, result in procedures that are unduly complicated, slow and expensive, and, at the same time, perhaps not conducive to developing all relevant information.
      2. All written communications addressed to the merits, received after notice of proposed rulemaking and in its course, from outside the agency by an agency or its personnel participating in the decision should be placed promptly in a file available for public inspection.
      3. Agencies should experiment in appropriate situations with procedures designed to disclose oral communications from outside the agency of significant information or argument respecting the merits of proposed rules, made to agency personnel participating in the decision on the proposed rule, by means of summaries promptly placed in the public file, meetings which the public may attend, or other techniques appropriate to their circumstances. To the extent that summaries are utilized they ordinarily should identify the source of the communications, but need not do so when the information or argument is cumulative.
     
      
      . See, e. g., United Steelworkers of America v. Marshall, 647 F.2d 1189, at 1237-1238 (D.C.Cir.1980) (interpreting our decision in Home Box Office as applying to “important communications that may have influenced the agency decisionmaking,” where “massive evidence” existed of secret lobbying, and the court was concerned that “independent discretion” of individual commissioners had not been exercised); Action for Children’s Television v. FCC, 564 F.2d 458, 476 (D.C.Cir.1977).
     
      
      . See text at nn.456-63 supra.
      
     
      
      . See Reform of Federal Regulations, Joint Report of the Committee on Governmental Affairs and the Committee on the Judiciary, S.Rep. No. 96-1018, 96th Cong., 2d Sess. 54-55 (1980):
      [There is] uncertainty at the agency level as to the appropriate procedures for dealing with ex parte communications in informal rulemaking. Several agencies have severely restricted ex parte communications while others have taken no action. The Division . on Administrative Law and Agency Practice of the District of Columbia Bar (Division I), after conducting a survey of federal agency ex parte contact procedures, reported to the Committee that “a number of agencies have not adopted procedures or policies of any kind, and practitioners appearing before these agencies consequently have little or no idea of the standards which they are expected to observe.” The Division also observed that several agencies with ex parte policies have articulated them in internal memoranda not generally available to the public during the development of their policies or after-wards. The Administrative Conference has also reported to the Committee that while numerous agencies have experimented with procedures to deal with ex parte communications, several major departments and agencies have not yet done so.
      The Committee has concluded that the best approach to the ex parte communications problem is to allow each agency to experiment with its own procedures both with respect to ex parte contacts from the public and from other agencies within the government.
      The Committee agrees with the conclusion of Division I of the D.C. Bar:
      “Legislation requiring each agency to develop regulations will insure that the subject of ex parte contacts receives the careful attention it deserves and that agencies develop consistent and clearly articulated policies to guide their own staffs and practitioners appearing before them. In addition, the experience of agencies in enacting and implementing regulations concerning ex parte contacts will provide the Congress, the courts, the public and the agencies themselves with a better understanding of the complex issues which this area involves.... ”
      Since the permissibility of ex parte communications affects the rights of the public to participate effectively in the formulation of agency rules, the Committee feels that the public should have the right to participate in the development of ex parte rules in the notice and comment proceedings required by Section 202.
     
      
      . See text accompanying nn.464-73 supra. Courts have upheld agency action against challenges based on alleged ex parte contacts by accepting the agency’s statement that it based its decision only upon the public record and ignored the allegedly improper contacts. See, e. g., Rogers Radio Communication Services, Inc. v. FCC, 593 F.2d 1225, 1233-34 (D.C.Cir. 1978); Eastern Air Lines, Inc. v. CAB, 271 F.2d 752, 758-59 (2d Cir. 1959), cert. denied, 362 U.S. 970, 80 S.Ct. 954, 4 L.Ed.2d 901 (1960).
     
      
      . See text accompanying nn.428-53 supra.
      
     
      
      . These materials, although docketed, are excluded from the “record for judicial review.” 42 U.S.C. § 7607(d)(7)(A). The logic of this exclusion of final draft comments from the agency’s “record for judicial review” is not completely clear, but we believe it evinces a Congressional intent for the reviewing court to judge the rule solely upon the data, information, and comments provided in the public docket, as well as the explanations EPA provides when it promulgates the rule, and not to concern itself with who in the Executive Branch advised whom about which policies to pursue. See generally Industrial Union Dept. v. Amer. Petroleum Institute, 448 U.S. 607, 100 S.Ct. 2844, 2858 n.31, 65 L.Ed.2d 1010 (1980).
      Of course, Executive Branch personnel are not exempt from the requirement of § 7607(d)(4)(B)(i), that all written materials received from “any person” during the comment period shall be placed in the docket. See 42 U.S.C. § 7602(e).
     
      
      . In this case we need not decide the effect upon rulemaking proceedings of a failure to disclose so-called “conduit” communications, in which administration or inter-agency contacts serve as mere conduits for private parties in order to get the latter’s off-the-record views into the proceeding. EDF alleges that many of the executive comments here fell into that category. Brief for Petitioner EDF at 21, 29, 43. We note that the Department of Justice Office of Legal Counsel has taken the position that it may be improper for White House advisers to act as conduits for outsiders. It has therefore recommended that Council of Economic Advisers officials summarize and place in rulemaking records a compilation of all written or oral comments they receive relevant to particular proceedings. See Office of Legal Counsel, Department of Justice, Memorandum for Hon. Cecil D. Andrus, Secretary of Interior, Re: Consultation With Council of Economic Advisers Concerning Rulemaking Under Surface Mining Control and Reclamation Act (undated), reprinted in Legal Times of Washington, January 29, 1979, at 32-3. EDF has given us no reason to believe that a policy similar to this was not followed here, or that unrecorded conduit communications exist in this case; we therefore decline to authorize further discovery simply on the unsubstantiated hypothesis that some such communications may be unearthed thereby. Cf. Citizens to Preserve Overton Park, Inc. v. Volpe, 401 U.S. 402, 420, 91 S.Ct. 814, 825, 28 L.Ed.2d 136 (1971); n.450 supra.
      
     
      
      . See The Federalist No. 70 (A. Hamilton); 1 M. Farrand, The Records of the Federal Convention of 1787, at 65-73, 93 (1937); 2 id. at 542; C. Thach, The Creation of the Presidency 1775-1789 (1923); E. Corwin, The President— Office and Powers 3-30 (1957); see generally G. Schubert, The Presidency in the Courts (1957).
     
      
      . U.S. Constitution, Art. II, §§ 2, 3; United States v. Nixon, 418 U.S. 683, 708, 94 S.Ct. 3090, 3107, 41 L.Ed.2d 1039 (1974) (privilege of confidentiality for conversations between the president and his staff “is fundamental to the operation of Government and inextricably rooted in the separation of powers under the Constitution”); Myers v. United States, 272 U.S. 52, 47 S.Ct. 21, 71 L.Ed. 160 (1926) (attempted Congressional limitation upon the President’s power to remove postmaster held unconstitutional); cf. Humphrey’s Executor v. United States, 295 U.S. 602, 55 S.Ct. 869, 79 L.Ed. 1611 (1935) (President may not remove an FTC Commissioner — a non-executive officer — without complying with a statutory for-cause requirement). See Verkuil, supra note 485, at 952-62.
     
      
      . See generally Reorganization Plan No. 3 of 1970, 84 Stat. 2086 (effective Dec. 2, 1970); 5 U.S.C. § 901 et seq., H.R.Doc. No. 134, 95th Cong., 1st Sess. 2, 115 (1976); Bruff, Presidential Power and Administrative Rulemaking, 88 Yale L.J. 451, 488-99 (1979).
     
      
      . The ordinary duties of officers prescribed by statute come under‘the general administrative control of the President by virtue of the general grant to him of the executive power, and he may properly supervise and guide their construction of the statutes under which they act in order to secure that unitary and uniform execution of the law which Article II of the Constitution evidently contemplated in vesting general executive power in the President alone. Laws are often passed with specific provision for the adoption of regulations by a department or bureau head to make the law workable and effective. The ability and judgment manifested by the official thus empowered ... are subjects which the President must consider and supervise in his administrative control.
      
        Myers v. United States, 272 U.S. 52, 135, 47 S.Ct. 21, 31, 71 L.Ed. 160 (1926).
     
      
      . See generally ABA Comm, on Law and the Economy, Federal Regulation: Roads to Reform 73-88 (1979); Cutler & Johnson, Regulation and the Political Process, 84 Yale L,J. 1395 (1975). Cf. Delegation'and Regulatory Reform: Letting the President Change the Rules, 89 Yale L.J. 561 (1980) (criticizing ABA, Cutler & Johnson proposals).
     
      
      . See generally Del Duca, supra note 8; C. Schultze, The Public Use of Private Interest 9-10 (1977):
      In the field of energy and the environment the generally accepted objectives of national policy imply a staggeringly complex and interlocking set of actions, directly affecting the production and consumption decisions of every citizen and every business firm. Consider for a moment the chain of collective decisions and their effects just in the case of electric utilities. Petroleum imports can be conserved by switching from oil-fired to coal-fired generation. But barring other measures, burning high-sulfur Eastern coal substantially increases pollution. Sulfur can be “scrubbed” from coal smoke in the stack, but at a heavy cost, with devices that turn out huge volumes of sulfur wastes that must be disposed of and about whose reliability there is some question. Intermittent control techniques (installing high smokestacks and switching off burners when meterological conditions are adverse) can, at lower cost, reduce local concentrations of sulfur oxides in the air, but cannot cope with the growing problem of sulfates and widespread acid rainfall. Use of low-sulfur Western coal would avoid many of these problems, but this coal is obtained by strip mining. Strip-mining reclamation is possible, but substantially hindered in large areas of the West by lack of rainfall. Moreover, in some coal-rich areas the coal beds form the underground aquifer and their removal could wreck adjacent farming or ranching economies. Large coal-burning plants might be located in remote areas far from highly populated urban centers in order to minimize the human effects of pollution. But such areas are among the few left that are unspoiled by pollution and both environmentalists and the residents (relatively few in number compared with those in metropolitan localities but large among the voting population in the particular states) strongly object to this policy. Fears, realistic or imaginary, about safety and about accumulation of radioactive waste have increasingly hampered the nuclear option.
     
      
      . Myers v. United States, 272 U.S. 52, 135, 47 S.Ct. 21, 31, 71 L.Ed. 160 (1926) (“there may be duties of a quasi-judicial character imposed on executive tribunals whose decisions after hearings affect the interest of individuals, the discharge of which the President cannot in a particular case properly influence or control”). See generally Verkuil, supra note 485, at 989; nn.499, 500 and accompanying text, supra.
      
     
      
      . 42 U.S.C. § 7607(d)(6)(C). ACUS has formally recommended the following as a general policy for intra-Executive Branch communications;
      1. Any Executive department or agency engaged in informal rulemaking in accordance with the procedural requirements of section 553 of the Administrative Procedure Act should be free to receive written or oral policy advice and recommendations at any time from the President, advisers to the President, the Executive Office of the President, and other administrative bodies, without having a duty to place these intragovemmental communications in the public file of the rule-making proceeding except to the extent called for in paragraph 2.
      2. When the rulemaking agency receives communications from the President, advisers to the President, the Executive Office of the President, or other administrative bodies which contain material factual information (as distinct from indications of governmental policy) pertaining to or affecting a proposed rule, the agency should promptly place copies of the documents, or summaries of any oral communications, in the public file of the rulemaking proceeding. All communications from these sources containing or reflecting comments by persons outside the government should be so identified and placed in the public file, regardless of their content. A rulemaking agency should consider the importance of giving public participants adequate opportunity to respond if the material presents new and important issues or creates serious conflicts of data.
      3. The Administrative Conference takes no position in the present recommendation concerning rulemaking by other than Executive departments and agencies.
      45 Fed.Reg. 86407, 86408 (Dec. 31, 1980) (emphasis supplied) (Admin.Conf. of the United States, Recommendation on Intragovemmental Communications in Informal Rulemaking, Rec. No. 80-6, issued Dec. 23, 1980). See also Verkuil, supra note 485, at 988 (suggesting that neither the existence nor the substance of personal Presidential communications should be recorded, but that in the case of White House staff contacts, only the substance of such contacts should be shielded from disclosure); Bruff, supra note 523, at 504-05 (suggesting that essentially all White House communications should be added to the public record).
     
      
      . See EPA Denial of Petitions for Reconsideration, 45 Fed.Reg. 8210, 8214-15 (Feb. 6, 1980) (“the Administrator’s decision on the emission ceiling was not based on any information not in the docket”). See generally Industrial Union Dept. v. Amer. Petroleum Institute, 448 U.S. 607, 100 S.Ct. 2844, 2858 n.31, 65 L.Ed.2d 1010 (1980) (“As we have often held, the validity of an agency’s determination must be judged on the basis of the agency’s stated reasons for making that determination”).
     
      
      . 42 U.S.C. § 7607(d)(6)(C) (emphasis supplied).
     
      
      . See Verkuil, supra note 485, at 981 & n.204. But cf. 42 U.S.C. § 7607(d)(6), (d)(3)(C) (requiring that promulgated rule be accompanied by statement of basis and purpose which includes a summary of major legal interpretations and policy considerations underlying the rule, and an explanation of major changes in promulgated rule from proposed rule, along with responses to significant criticisms or new data).
     
      
      . These meetings were held on April 23 and May 2, 1979. See text at nn.436-38, 448-49 supra.
      
     
      
      . EDF relies heavily upon Pillsbury Co. v. FTC, 354 F.2d 952 (5th Cir. 1966), and Koniag, Inc. v. Andrus, 580 F.2d 601 (D.C.Cir.), cert. denied, 439 U.S. 1052, 99 S.Ct. 733, 58 L.Ed.2d 712 (1978). Neither case is apposite to the facts here. In Pillsbury, several Senators on the Antitrust and Monopoly Subcommittee of the Senate Judiciary Committee expressed strong opinions on a key issue in the Pillsbury case then pending before the FTC. In its subsequent decision, the FTC ruled as the members of the Senate committee had suggested. The court, basing its holding on the fact that the agency was carrying out “its judicial function,” found that the “private litigants” in the case had a right “to a fair trial” and “to the appearance of impartiality” when the agency was acting in such capacity. 354 F.2d at 964. Therefore procedural due process required a reversal of the agency’s decision.
      In Koniag, a letter was sent from a Congressman to the Secretary of the Interior about an adjudicatory, adversary proceeding which concerned the eligibility of certain Alaskan villages to take land and revenues under the Alaskan Native Claims Settlement Act. The letter requested the Secretary to postpone his decision on the cases pending a review and opinion by the Comptroller General, because it “appears from the testimony [at the hearings] . . . that certain villages should not have been certified as eligible for land selections under ANCSA.” 580 F.2d at 610. This court found that the letter compromised the appearance of the Secretary’s impartiality. Id. Both Pillsbury and Koniag are easily distinguishable on the grounds explained earlier, see text at nn.499ff. supra. Cf. American Public Gas Ass’n v. FPC, 567 F.2d 1016, 1070 (D.C.Cir.1977), cert. denied, 435 U.S. 907, 98 S.Ct. 1456, 55 L.Ed.2d 499 (1978) (during FPC ratesetting proceeding, Congressional subcommittee questioning and criticism of Commissioners did not in this case result in unlawful interference with the Commission’s independence); Environmental Defense Fund, Inc. v. Blum, 458 F.Supp. 650, 662-63 (D.D.C.1978) (during informal rulemaking, communications from Congressmen which were directly relevant to the agency’s proceedings did not reflect any impropriety).
     
      
      . 459 F.2d 1231 (D.C.Cir.1971), cert. denied, 405 U.S. 1030, 92 S.Ct. 1290, 31 L.Ed.2d 489 (1972).
     
      
      . 459 F.2d at 1246.
     
      
      . Id. at 1249.
     
      
      . Id. at 1246.
     
      
      . Id. at 1246-47.
     
      
      . The only hint we are provided that extraneous “threats” were made comes from a newspaper article which states, in part,
      The ceiling decision came after two weeks of what one Senate source called “hard-ball arm-twisting” by Byrd and other coal state Senators. Byrd summoned Costle and White House adviser Stuart Eizenstat strongly hinting that the Administration needs his support on strategic arms limitation treaty (SALT) and the windfall profits tax, according to Senate and Administration sources.
      
        The Washington Post, May 5, 1979, at A-l (emphasis supplied). We do not believe that a single newspaper account of strong “hint[s]” represents substantial evidence of extraneous pressure significant enough to warrant a finding of unlawful congressional interference.
     
      
      . Cf. Rodgers, Judicial Review of Risk Assessments: The Role of Decision Theory in Unscrambling the Benzene Decision, 11 Envt’l L. 301, 302, 309 (1981) (“[T]he suspicion has arisen, certainly among practitioners who can say such things, that the grand synthesizing principle that tells us whether the court will dig deeply or bow cursorily depends exclusively on whether the judge agrees with the result of the administrative decision.... Few practitioners believe that judges read, much less studiously follow, the monstrous records thrust before them. Nor do these records deserve reading, contrived and formless as they are”).
     
      
      . See H.R.Rep. No. 95-294, supra note 47, at 318, 4 L.H. 2785.