Under § 301(b) of the Federal Water Pollution Control Act,
the Environmental Protection Agency (EPA) is to set 1977 effluent
limitations for categories of point sources, requiring such sources
to meet standards based on application of the "best practicable
control technology currently available" (BPT), and 1987
limitations, requiring all point sources to meet standards based on
application of the "best available technology economically
achievable" (BAT). Section 301(c) of the Act provides for variances
from 1987 BAT effluent limitations for individual point sources
upon a showing "that such modified requirements (1) will represent
the maximum use of technology within the economic capability of the
owner or operators; and (2) will result in reasonable further
progress toward the elimination of the discharge of pollutants."
However, the Act contains no similar variance provision authorizing
consideration of the economic ability of the individual operator to
meet the cost of complying with 1977 BPT standards. In 1977, the
EPA promulgated BPT pollution discharge limitations for the coal
mining industry and for certain portions of the mineral mining and
processing industry. Under the regulations, a greater than normal
cost of implementation will be considered in acting on a request
for a variance, but a variance will not be granted on the basis of
the applicant's economic inability to meet the cost of implementing
the uniform standard. Respondents sought review of the regulations
in various Courts of Appeals, challenging both the substantive
standards and the variance clause. All of the petitions were
transferred to the Court of Appeals for the Fourth Circuit, which
set aside the variance provision as unduly restrictive and required
the EPA to consider,
inter alia, the factors set out in
§ 301(c), including the applicant's economic capability.
Held: The Court of Appeals erred in not accepting the EPA's
interpretation of the Act. The EPA is not required by the Act to
consider economic
Page 449 U. S. 65
capability in granting variances from its uniform BPT standards.
Pp.
449 U. S.
73-85.
(a) The statute's plain language does not support the Court of
Appeals' position. Section 301(c)'s requirement for a BAT variance
of "reasonable further progress" toward the elimination of
pollutant discharges refers to the prior BPT standard, but there is
no comparable prior standard with respect to BPT limitations. And
since BPT limitations do not require an industrial category to
commit the maximum resources economically possible to pollution
control, even if affordable, the § 301(c) BAT variance factor
as to the maximum use of technology within the applicant's economic
capability is inapposite in the BPT context. More importantly,
under the Act, the Administrator of the EPA, in determining BPT
limitations, is directed to consider the benefits of effluent
reductions as compared to the cost of pollution control in defining
the best practicable technology at a level that would effect the
1977 goal of substantially reducing total pollution produced by
each industrial category. Thus, the statute contemplated
regulations that would require a substantial number of point
sources with the poorest performances either to conform to BPT
standards or to cease production. To allow a BPT variance based on
economic capability and not to require adherence to the prescribed
minimum technology would permit the employment of the very
practices that the Administrator had rejected in establishing the
best practicable technology currently available in the industry.
Pp.
449 U. S.
73-78.
(b) The EPA's interpretation of the statutory language is also
supported by the legislative history, which shows that Congress
understood that the economic capability provision of § 301(c)
was limited to BAT variances; foresaw and accepted the economic
hardship, including the closing of some plants, that BPT effluent
limitations would cause; and took certain steps to alleviate this
hardship, steps which did not include allowing a BPT variance based
on economic capability. Pp.
449 U. S.
79-83.
(c) In the face of § 301(c)'s explicit limitation to BAT
variances and in the absence of any other specific direction in the
statute to provide for BPT variances in connection with permits for
individual point sources, the Administrator adopted a reasonable
construction of the statutory mandate, and the Court of Appeals
erred in concluding that, since BAT limitations are to be more
stringent than BPT limitations, the variance provision for the
latter must be at least as flexible as that for the former with
respect to affordability. Pp.
449 U. S.
83-84.
601 F.2d 111 and 604 F.2d 239, reversed.
Page 449 U. S. 66
WHITE, J., delivered the opinion of the Court, in which all
other Members joined, except POWELL, J., who took no part in the
consideration or decision of the cases.
JUSTICE WHITE delivered the opinion of the Court.
In April and July, 1977, the Environmental Protection Agency
(EPA), acting under the Federal Water Pollution Control Act (Act),
as amended, 86 Stat. 816, 33 U.S.C. § 1251
et seq.,
promulgated pollution discharge limitations for the coal mining
industry and for that portion of the mineral mining and processing
industry comprising the crushed stone, construction sand, and
gravel categories. [
Footnote 1]
Although the Act does not expressly authorize or require variances
from the 1977 limitation, each set of regulations contained a
variance provision. [
Footnote
2] Respondents sought review of the regulations in
Page 449 U. S. 67
various Courts of Appeals, challenging both the substantive
standards and the variance clause. [
Footnote 3] All of the petitions for review were
transferred to the Court of Appeals for the Fourth Circuit. In
National Crushed Stone Assn. v. EPA, 601 F.2d 111 (1979),
and in
Consolidation Coal Co. v. Costle, 604 F.2d 239
(1979), the Court of Appeals set aside the
Page 449 U. S. 68
variance provision as "unduly restrictive" and remanded the
provision to EPA for reconsideration. [
Footnote 4]
To obtain a variance from the 1977 uniform discharge
limitations, a discharger must demonstrate that the
"factors relating to the equipment or facilities involved, the
process applied, or other such factors relating to such discharger
are fundamentally different from the factors considered in the
establishment of the guidelines."
Although a greater than normal cost of implementation will be
considered in acting on a request for a variance, economic ability
to meet the costs will not be considered. [
Footnote 5] A variance, therefore, will not be granted
on the basis of the applicant's economic inability to meet the
costs of implementing the uniform standard.
The Court of Appeals for the Fourth Circuit rejected this
position. It required EPA to "take into consideration, among other
things, the statutory factors set out in § 301(c)," which
authorizes variances from the more restrictive pollution
limitations to become effective in 1987 and which specifies
economic capability as a major factor to be taken into account.
[
Footnote 6] The court held
that
"'if [a plant] is doing all that the maximum use of
Page 449 U. S. 69
technology within its economic capability will permit, and if
such use will result in reasonable further progress toward the
elimination of the discharge of pollutants . . . no reason appears
why [it] should not be able to secure such a variance should it
comply with any other requirements of the variance.'"
601 F.2d at 124, quoting from
Appalachian Power Co. v.
Train, 545 F.2d 1351, 1378 (CA4 197).
We granted certiorari to resolve the conflict between the
decisions below and
Weyerhaeuser Co. v. Costle, 191
U.S.App.D.C. 309, 590 F.2d 1011 (1978), in which the variance
provision was upheld. 444 U.S. 1069.
I
We shall first briefly outline the basic structure of the Act,
which translates Congress' broad goal of eliminating "the discharge
of pollutants into the navigable waters," 33 U.S.C. §
1251(a)(1), into specific requirements that must be met by
individual point sources. [
Footnote
7]
Section 301(b) of the Act, 33 U.S.C. § 1311(b) (1976 ed.
and Supp. III), authorizes the Administrator to set effluent
limitations for categories of point sources. [
Footnote 8] With respect to existing point
sources, the section provides for implementation of increasingly
stringent effluent limitations in two steps. The first step to be
accomplished by July 1, 1977, requires all point sources to meet
standards based on "the application of
Page 449 U. S. 70
the best practicable control technology currently available
[BPT] as defined by the Administrator. . . ." § 31(b)(1)(A).
The second step, to be accomplished by July 1, 1987, requires all
point sources to meet standards based on application of the "best
available technology economically achievable [BAT] for such
category or class. . . ." [
Footnote
9] § 301(b)(2)(A). Both sets of limitations -- BPT's
followed within 10 years by BAT's -- are to be based upon
regulatory guidelines established under § 304(b).
Section 304(b) of the Act, 33 U.S.C. § 1314(b), is again
divided into two sections corresponding to the two levels of
technology, BPT and BAT. Under § 304(b)(1), the Administrator
is to quantify
"the degree of effluent reduction attainable through the
application of the best practicable control technology currently
available [BPT] for classes and categories of point sources. . .
."
In assessing the BPT, the Administrator is to consider
"the total cost of application of technology in relation to the
effluent reduction benefits to be achieved from such application, .
. . the age of equipment and facilities involved, the process
employed, the engineering aspects of the application of various
types of control techniques, process changes, non-water quality
environmental impact (including energy requirements), and such
other factors as the Administrator deems appropriate."
33 U.S.C. § 1314(b)(1)(b).
Page 449 U. S. 71
Similar directions are given the Administrator for determining
effluent reductions attainable from the BAT, except that, in
assessing BAT, total cost is no longer to be considered in
comparison to effluent reduction benefits. [
Footnote 10]
Section 402 authorizes the establishment of the National
Pollutant Discharge Elimination System (NPDES), under which every
discharger of pollutants is required to obtain a permit. The permit
requires the discharger to meet all the applicable requirements
specified in the regulations issued under § 301. Permits are
issued by either the Administrator or state agencies that have been
approved by the Administrator. [
Footnote 11] The permit
"transform[s] generally applicable effluent limitations . . .
into the obligations (including a timetable for compliance) of the
individual discharger. . . ."
EPA v. California ex rel. State Water Resources Control
Board, 426 U. S. 200,
426 U. S. 205
(1976).
Section 301(c) of the Act explicitly provides for modifying the
1987 (BAT) effluent limitations with respect to individual point
sources. A variance under § 301(c) may be obtained upon a
showing
"that such modified requirements (1) will represent the maximum
use of technology within the economic capability of the owner or
operator; and (2) will result in reasonable further progress toward
the elimination
Page 449 U. S. 72
of the discharge of pollutants."
Thus, the economic ability of the individual operator to meet
the costs of effluent reductions may in some circumstances justify
granting a variance from the 1987 limitations.
No such explicit variance provision exists with respect to BPT
standards, but in
E. I. du Pont de Nemours Co. v. Train,
430 U. S. 112
(1977), we indicated that a variance provision was a necessary
aspect of BPT limitations applicable by regulations to classes and
categories of point sources.
Id. at
430 U. S. 128.
The issue in this case is whether the BPT variance provision must
allow consideration of the economic capability of an individual
discharger to afford the costs of the BPT limitation. For the
reasons that follow, our answer is in the negative. [
Footnote 12]
Page 449 U. S. 73
II
The plain language of the statute does not support the position
taken by the Court of Appeals. Section 301(c) is limited on its
face to modifications of the 1987 BAT limitations. It says nothing
about relief from the 1977 BPT requirements. Nor does the language
of the Act support the position that, although § 301(c) is not
itself applicable to BPT standards, it requires that the
affordability of the prescribed 1977 technology be considered in
BPT variance decisions. [
Footnote 13]
Page 449 U. S. 74
This would he a logical reading of the statute only if the
factors listed in § 301(c) bore a substantial relationship to
the considerations underlying the 1977 limitations as they do to
those controlling the 1987 regulations. This is not the case.
The two factors listed in § 301(c) -- "maximum use of
technology within the economic capability of the owner or operator"
and "reasonable further progress toward the elimination of the
discharge of pollutants" -- parallel the general definition of BAT
standards as limitations that
"require application of the best available technology
economically achievable for such category or class, which will
result in reasonable further progress toward . . . eliminating the
discharge of all pollutants. . . ."
§ 301(b)(2). A § 301(c) variance, thus, creates for a
particular point source a BAT standard that represents for it the
same sort of economic and technological commitment as the general
BAT standard creates for the class. As with the general BAT
standard, the variance assumes that the 1977 BPT standard has been
met by the point source and that the modification represents a
commitment of the maximum resources economically possible to the
ultimate goal of eliminating all polluting discharges.
Page 449 U. S. 75
No one who can afford the best available technology can secure a
variance.
There is no similar connection between § 301(c) and the
considerations underlying the establishment of the 1977 BPT
limitations. First, § 301(c)'s requirement of "reasonable
further progress" must have reference to some prior standard. BPT
serves as the prior standard with respect to BAT. There is,
however, no comparable, prior standard with respect to BPT
limitations. [
Footnote 14]
Second, BPT limitations do not require an industrial category to
commit the maximum economic resources possible to pollution
control, even if affordable. Those point sources already using a
satisfactory pollution control technology need take no additional
steps at all. The § 301(c) variance factor, the "maximum use
of technology within the economic capability of the owner or
operator," would therefore be inapposite in the BPT context. It
would not have the same effect there that it has with respect to
BAT's,
i.e., it would not apply the general requirements
to an individual point source.
More importantly, to allow a variance based on the maximum
technology affordable by the point source, even if that technology
fails to meet BPT effluent limitations, would undercut the purpose
and function of BPT limitations. Rather than the 1987 requirement
of the best measures economically and technologically feasible, the
statutory provisions for 1977 contemplate regulations prohibiting
discharges from any point source in excess of the effluent produced
by the best practicable technology currently available
Page 449 U. S. 76
in the industry. The Administrator was referred to the industry
and to existing practices to determine BPT. He was to categorize
point sources, examine control practices in exemplary plants in
each category, and, after weighing benefits and costs and
considering other factors specified by § 304, determine and
define the best practicable technology at a level that would effect
the obvious statutory goal for 1977 of substantially reducing the
total pollution produced by each category of the industry.
[
Footnote 15] Necessarily,
if pollution is to be diminished, limitations based on BPT must
forbid the level of effluent produced by the most pollution-prone
segment of the industry, that segment not measuring up to "the
average of the best existing performance." So understood, the
statute contemplated regulations that would require a substantial
number of point sources with the poorest performances either to
conform to BPT standards or to cease production. To allow a
variance based on economic capability and not to require adherence
to the prescribed minimum technology would permit the employment of
the very practices that the Administrator had rejected in
establishing the best practicable technology currently in use in
the industry.
To put the matter another way, under § 304, the
Administrator is directed to consider the benefits of effluent
reductions as compared to the costs of pollution control in
determining BPT limitations. Thus, every BPT limitation represents
a conclusion by the Administrator that the costs imposed on the
industry are worth the benefits in pollution reduction
Page 449 U. S. 77
that will be gained by meeting those limits. To grant a variance
because a particular owner or operator cannot meet the normal costs
of the technological requirements imposed on him, and not because
there has been a recalculation of the benefits compared to the
costs, would be inconsistent with this legislative scheme and would
allow a level of pollution inconsistent with the Judgment of the
Administrator. [
Footnote
16]
In terms of the scheme implemented by BPT limitations, the
factors that the Administrator considers in granting variances do
not suggest that economic capability must also be a determinant.
The regulations permit a variance where
"factors relating to the equipment or facilities involved, the
process applied, or such other factors relating to such discharger
are fundamentally different from the factors considered in the
establishment of the guidelines."
If a point source can show that its situation, including its
costs of compliance, is not within the range of circumstances
considered by the Administrator, then it may receive a variance,
whether or not the source could afford to comply with the minimum
standard. [
Footnote 17] In
such situations, the variance is an acknowledgment
Page 449 U. S. 78
that the uniform BPT limitation was set without reference to the
full range of current practices, to which the Administrator was to
refer. Insofar as a BPT limitation was determined without
consideration of a current practice fundamentally different from
those that were considered by the Administrator, that limitation is
incomplete. A variance based on economic capability, however, would
not have this character: it would allow a variance simply because
the point source could not afford a compliance cost that is not
fundamentally different from those the Administrator has already
considered in determining BPT. It would force a displacement of
calculations already performed, not because those calculations were
incomplete or had unexpected effects, but only because the costs
happened to fall on one particular operator, rather than on another
who might be economically better off.
Because the 1977 limitations were intended to reduce the total
pollution produced by an industry, requiring compliance with BPT
standards necessarily imposed additional costs on the segment of
the industry with the least effective technology. If the statutory
goal is to be achieved, these costs must be borne or the point
source eliminated. In our view, requiring variances from otherwise
valid regulations where dischargers cannot afford normal costs of
compliance would undermine the purpose and the intended operative
effect of the 1977 regulations.
Page 449 U. S. 79
III
The Administrator's present interpretation of the language of
the statute is amply supported by the legislative history, which
persuades us that Congress understood that the economic capability
provision of § 301(c) was limited to BAT variances; that
Congress foresaw and accepted the economic hardship, including the
closing of some plants, that effluent limitations would cause; and
that Congress took certain steps to alleviate this hardship, steps
which did not include allowing a BPT variance based on economic
capability. [
Footnote
18]
There is no indication that Congress intended § 301(c) to
reach further than the limitations of its plain language. The
statement of the House managers of the Act described § 301(c)
as
"not intended to justify modifications which would not represent
an upgrading over the July 1, 1977, requirements of 'best
practicable control technology.'"
Leg.Hist. 232. The Conference Report noted that a § 301(c)
variance could only be granted after the effective date of BPT
limitations,
Page 449 U. S. 80
and could only be applied to BAT limitations. Similarly, the
Senate Report on the Conference action emphasized that one of the
purposes of the BPT limitation was to avoid imposing on the
"Administrator any requirement . . . to determine the economic
impact of controls on any individual plant in a single community."
Leg.Hist. 170.
Nor did Congress restrict the reach of § 301(c) without
understanding the economic hardships that uniform standards would
impose. Prior to passage of the Act, Congress had before it a
report jointly prepared by EPA, the Commerce Department, and the
Council on Environmental Quality on the impact of the pollution
control measures on industry. [
Footnote 19] That report estimated that there would be
200 to 300 plant closings caused by the first set of pollution
limitations. Comments in the Senate debate were explicit: "There is
no doubt that we will suffer some disruptions in our economy
because of our efforts; many marginal plants may be forced to
close." Leg.Hist. 1282 (Sen. Bentsen). [
Footnote 20] The House managers explained the
Conference position as follows:
"If the owner or operator of a given point source determines
that he would rather go out of business than meet the 1977
requirements, the managers clearly expect that any discharge issued
in the interim would reflect the fact that all discharges not in
compliance with such 'best practicable technology currently
available' would cease by June 30, 1977."
Id. at 231.
Congress did not respond to this foreseen economic impact by
making room for variances based on economic impact. In fact, this
possibility was specifically considered and rejected:
"The alternative [to a loan program] would be waiving strict
environmental standards where economic hardship
Page 449 U. S. 81
could be shown. But the approach of giving variances to
pollution controls based on economic grounds has long ago shown
itself to be a risky course: all too often, the variances become a
tool used by powerful political interests to obtain so many
exemptions for pollution control standards and timetables on the
filmsiest [
sic] of pretenses that they become meaningless.
In short, with variances, exceptions to pollution cleanup can
become the rule, meaning further tragic delay in stopping the
destruction of our environment."
Id. at 1355 (Sen. Nelson). Instead of economic
variances, Congress specifically added two other provisions to
address the problem of economic hardship.
First, provision was made for low-cost loans to small businesses
to help them meet the cost of technological improvements. 86 Stat.
898, amending § 7 of the Small Business Act, 15 U.S.C. §
636. The Conference Report described the provision as authorizing
the Small Business Administration
"to make loans to assist small business concerns . . . if the
Administrator determines that the concern is likely to suffer
substantial economic injury without such assistance."
Leg.Hist. 153. Senator Nelson, who offered the amendment
providing for these loans, saw the loans as an alternative to the
dangers of an economic variance provision that he felt might
otherwise be necessary. [
Footnote 21] Several Congressmen understood the loan
program as an alternative to forced closings:
"It is the smaller business that is hit hardest by these laws
and their enforcement. And it is that same class of business that
has the least resources to meet the demands of this enforcement. .
. . Without assistance, many of these businesses may face
extinction."
Id. at 1359 (Sen. McIntyre). [
Footnote 22]
Page 449 U. S. 82
Second, an employee protection provision was added, giving EPA
authority to investigate any plant's claim that it must cut back
production or close down because of pollution control regulations.
§ 507(e), 86 Stat. 890,33 U.S.C. 1367(e). [
Footnote 23] This provision had two
purposes: to allow EPA constantly to monitor the economic effect on
industry of pollution control rules and to undercut economic
threats by industry that would create pressure to relax effluent
limitation rules. [
Footnote
24] Representative Fraser explained this second purpose as
follows:
"[T]he purpose of the amendment is to provide for a public
hearing in the case of an industry claim that
Page 449 U. S. 83
enforcement of these water control standards will force it to
relocate or otherwise shut down operations. . . . I think too many
companies use the excuse of compliance, or the need for compliance,
to change operations that are going to change anyway. It is this
kind of action that gives the whole antipollution effort a bad
name, and causes a great deal of stress and strain in the
community."
Leg.Hist. 659.
The only protection offered by the provision, however, is the
assurance that there will be a public inquiry into the facts behind
such an economic threat. The section specifically concludes
that
"[n]othing in this subsection shall be construed to require or
authorize the Administrator to modify or withdraw any effluent
limitation or order issued under this chapter."
§ 507(e), 33 U.S.C. § 1367(e).
As we see it, Congress anticipated that the 1977 regulations
would cause economic hardship and plant closings: "[T]he question .
. . is not what a court thinks is generally appropriate to the
regulatory process; it is what Congress intended for
these
regulations."
Du Pont, 430 U.S. at
430 U. S.
138.
IV
It is by now a commonplace that,
"when faced with a problem of statutory construction, this Court
shows great deference to the interpretation given the statute by
the officers or agency charged with its administration."
Udall v. Tallman, 380 U. S. 1,
380 U. S. 16
(1965). [
Footnote 25] The
statute itself does not provide
Page 449 U. S. 84
for BPT variances in connection with permits for individual
point sources, and we had no occasion in
Du Pont to
address the adequacy of the Administrator's 1977 variance
provision. In the face of § 301(c)'s explicit limitation and
in the absence of any other specific direction to provide for
variances in connection with permits for individual point sources,
we believe that the Administrator has adopted a reasonable
construction of the statutory mandate.
In rejecting EPA's interpretation of the BPT variance provision,
the Court of Appeals relied on a mistaken conception of the
relation between BPT and BAT standards. The court erroneously
believed that, since BAT limitations are to be more stringent than
BPT limitations, the variance provision for the latter must be at
least as flexible as that for the former with respect to
affordability. [
Footnote 26]
The variances permitted by § 301(c) from the 1987 limitations,
however, can reasonably be understood to represent a cost in
decreased effluent reductions that can only be afforded once the
minimal standard expressed in the BPT limitation has been reached.
[
Footnote 27]
Page 449 U. S. 85
We conclude, therefore, that the Court of Appeals erred in not
accepting EPA's interpretation of the Act. EPA is not required by
the Act to consider economic capability in granting variances from
its uniform BPT regulations.
The Judgments of the Court of Appeals are Reversed.
JUSTICE POWELL took no part in the consideration or decision of
these cases.
* Together with
Costle, Administrator, Environmental
Protection Agency v. Consolidation Coal Co. et al., also on
certiorari to the same court (see this Court's Rule 19.4).
[
Footnote 1]
The coal mining standards were published at 42 Fed.Reg. 21380
et seq. (1977), adopting 40 CFR Part 434. The mineral
mining and processing standards were published at 42 Fed.Reg. 35843
et seq. (1977), adopting 40 CFR Part 436.
[
Footnote 2]
The variance provision reads as follows:
"In establishing the limitations set forth in this section, EPA
took into account all information it was able to collect, develop
and solicit with respect to factors (such as age and size of plant,
raw materials, manufacturing processes, products produced,
treatment technology available, energy requirements and costs)
which can affect the industry subcategorization and effluent levels
established. It is, however, possible that data which would affect
these limitations have not been available and, as a result, these
limitations should be adjusted for certain plants in this industry.
An individual discharger or other interested person may submit
evidence to the Regional Administrator (or to the State, if the
State has the authority to issue NPDES permits) that factors
relating to the equipment or facilities involved, the process
applied, or other such factors related to such discharger are
fundamentally different from the factors considered in the
establishment of the guidelines. On the basis of such evidence or
other available information, the Regional Administrator (or the
State) will make a written finding that such factors are or are not
fundamentally different for that facility compared to those
specified in the Development Document. If such fundamentally
different factors are found to exist, the Regional Administrator or
the State shall establish for the discharger effluent limitations
in the NPDES permit either more or less stringent than the
limitations established herein, to the extent dictated by such
fundamentally different factors. Such limitation must be approved
by the Administrator of the Environmental Protection Agency. The
Administrator may approve or disapprove such limitations, specify
other limitations, or initiate proceedings to revise these
regulations."
See 40 CFR § 434.22 (1980) (coal preparation
plants); § 434.32 (acid mine drainage); § 434.42
(alkaline mine drainage); § 436.22 (crushed stone) and §
436.32 (construction sand and gravel).
[
Footnote 3]
The actions were brought under § 509(b)(1)(E), which, as
set forth in 33 U.S.C. § 1369(b)(1)(E), gives the courts of
appeals jurisdiction to review "the Administrator's action . . . in
approving or promulgating any effluent limitation or other
limitation under section 1311 . . . of this title. . . ."
Plaintiffs in
National Crushed Stone were three producers
and their trade association. Plaintiffs in
Consolidation
Coal were 17 coal producers, their trade association, 5
citizens' environmental associations, and the Commonwealth of
Pennsylvania.
[
Footnote 4]
In
National Crushed Stone, the Court of Appeals also
vacated and remanded the substantive regulations. That action is
not before the Court. In
Consolidation Coal, the
substantive regulations were upheld.
[
Footnote 5]
EPA has explained its position as follows:
"Thus, a plant may be able to secure a BPT variance by showing
that the plant's own compliance costs with the national guideline
limitation would be x times greater than the compliance costs of
the plants EPA considered in setting the national BPT limitation. A
plant may not, however, secure a BPT variance by alleging that the
plant's own financial status is such that it cannot afford to
comply with the national BPT limitation."
43 Fed.Reg. 50042 (1978).
[
Footnote 6]
Section 301(c), 86 Stat. 844, 33 U.S.C. § 1311(c), allows
the Administrator to grant a variance
"upon a showing by the owner or operator . . . that such
modified requirements (1) will represent the maximum use of
technology within the economic capability of the owner or operator;
and (2) will result in reasonable further progress toward the
elimination of the discharge of pollutants."
[
Footnote 7]
A "point source" is defined as "any discernible, confined and
discrete conveyance, . . . from which pollutants are or may be
discharged." § 502(14), 33 U.S.C. § 1362(14) (1976 ed.,
Supp. III).
[
Footnote 8]
Throughout this opinion, "Administrator" refers to the
Administrator of EPA. In
E. I. du Pont de Nemours & Co. v.
Train, 430 U. S. 112
(1977), we sustained the Administrator's authority to issue the
1977 effluent limitations.
[
Footnote 9]
The Federal Water Pollution Control Act Amendments of 1972, 86
Stat. 816, required that the second-stage standards be met by 1983.
This deadline was extended in the Clean Water Act of 1977, 91 Stat.
1567. Depending on the nature of the pollutant, the deadline for
the more stringent limitations now falls between July 1, 1984, and
July 1, 1987. The 1977 Act also replaced the BAT standard with a
new standard, "best conventional pollutant control technology [BCT]
," for certain so-called "conventional pollutants." 33 U.S.C.
§ 1311(b)(2)(1) (1976 ed., Supp. III). The distinction between
BCT and BAT is not relevant to the issue presented here.
[
Footnote 10]
Senator Muskie, the principal Senate sponsor of the Act,
described the "limited cost-benefit analysis" employed in setting
BPT standards as being intended to
"limit the application of technology only where the additional
degree of effluent reduction is wholly out of proportion to the
costs of achieving such marginal level of reduction. . . ."
Remarks of Senator Muskie reprinted in Legislative History of
the Water Pollution Control Act Amendments of 1972 (Committee Print
compiled for the Senate Committee on Public Works by the Library of
Congress) Ser. No. 93-1, p. 170 (1973) (hereafter Leg.Hist.).
Section 304(b)(2)(b) lists "cost" as a factor to consider in
assessing BAT, although it does not state that costs shall be
considered in relation to effluent reduction.
[
Footnote 11]
Establishment of state permit programs is authorized by §
402(b), 33 U.S.C. § 1342(b) (1976 ed., Supp. III). At present,
over 30 States and covered territories operate their own NPDES
programs.
[
Footnote 12]
In
Du Pont, we held that preenforcement review of the
BPT variance provision would be "premature," 430 U.S. at
430 U. S. 128,
n.19. In its petition for certiorari in this case, EPA argued that
the Court of Appeals erred in reviewing the variance clause prior
to application of the regulation to a particular discharger's
request for a variance. EPA has now abandoned this position. We
agree with the Court of Appeals that whatever may have been true at
the time of
Du Pont, preenforcement review of the variance
provision is no longer premature, since EPA has now taken the
definitive position that the factors specified in § 301(c)
apply only to BAT limitations, and not to BPT limitations.
See 43 Fed.Reg. 44847-44848, 50042 (1978); 44 Fed.Reg.
32893-32894 (1979).
But cf. n 25,
infra. The Court of Appeals for the
District of Columbia Circuit reached the same conclusion in
considering the identical variance clause in the context of BPT
standards for paper mills:
"In the three years that have now elapsed since
du Pont
was briefed and argued in the Fourth Circuit, however, enough
indicia of the Agency's attitude toward the 1977 variance provision
under the Act has [
sic] accumulated so that its
administration is anything but 'a matter of speculation.'"
Weyerhaeuser Co. v. Costle, 191 U.S.App.D.C. 309, 330,
590 F.2d 1011, 1032 (1978) (citation omitted).
This is the proper result under the twofold test articulated in
Abbott Laboratories v. Gardner, 387 U.
S. 136,
387 U. S. 149
(1967), for evaluating the ripeness of administrative action.
First, the issue is "fit" for judicial decision, because it
involves only a question of law: whether the Court of Appeals
properly construed the Act to require EPA to consider § 301(c)
factors in granting BPT variances. Second, failure to review the
variance issue now would cause "hardship" to the parties. The
regulations in question affect thousands of point sources
throughout the country -- about 4,800 crushed-stone facilities and
6,000 coal facilities, many of them involved in this case through
their trade associations. The resolution of this conflict will
determine for some of these plants whether they will continue to
exist or not, and, for many others, it will determine the level of
funding they must budget for pollution controls. They should not be
left to speculate on what the regulations require of them.
Similarly, EPA represents to the Court that a failure to resolve
the issue will cause some hardship to EPA: "a present ruling . . .
would advance, rather than impede, the administrative enforcement
of the Act." Brief for Petitioners 1, n. 17.
Moreover, in
Du Pont, supra, we held that a uniform BPT
effluent regulation must contain a variance provision, if it is to
be valid. EPA has definitively stated that economic capability will
not be a ground for a variance. Section 509(b)(1)(E) provides for
judicial review of effluent limitations promulgated pursuant to
§ 301, and these actions were brought under that section.
Since the variance clause is an integral part of the regulation,
review of the regulation must reach the question of whether this
limitation on the scope of the variance provision renders the
regulation invalid under
Du Pont.
Finally, the fact that the Court of Appeals for the Fourth
Circuit held the variance provision to be invalid, while the Court
of Appeals for the District of Columbia Circuit in
Weyerhaeuser, supra, upheld the same provision, provides
yet another reason for this Court to settle this controversy at
this time. For all of these reasons, the issue is ripe for judicial
review.
[
Footnote 13]
It is true that, in
Du Pont, we said there "[was no]
radical difference in the mechanism used to impose limitations for
the 1977 and the 198[7] deadlines" and that "there is no indication
in either § 301 or § 304 that the § 304 guidelines
play a different role in setting 1977 limitations." 430 U.S. at
430 U. S. 127.
But our decision in
Du Pont was that the 1977 limitations,
like the 1987 limitations, could be set by regulation and for
classes of point sources. It dealt with the power of the
Administrator and the procedures he was to employ. There was no
suggestion, nor could there have been, that the 1977 BPT and the
1987 BAT limitations were to have identical purposes or content. It
follows that no proper inference could be drawn from
Du
Pont that the grounds for issuing variances from the 1987
limitations should also be the grounds for permitting individual
point sources to depart from 1977 standards. Indeed, our opinion
recognized that § 301(c) was designed for BAT limitations, 430
U.S. at
430 U. S. 121,
430 U. S. 127,
n. 17. Had we thought that § 301(c) governed variances from
both the BAT and BPT standards, there would have been no need to
postpone to another day, as we did in 430 U.S. at
430 U. S. 128,
n.19, the question whether the variance clause contained in the
1977 regulations had the proper scope. That scope would have been
defined by § 301(c).
[
Footnote 14]
Also, the ultimate goal expressed in § 301(c), "the
elimination of the discharge of pollutants," reflects the "national
goal" specified in § 301(b)(2)(A) of "eliminating the
discharge of all pollutants." This is not the aim of a BPT
limitation; its more modest purpose is to effect a first step
toward this goal. Thus, while BAT limitations may be regarded as
falling between a level of effluent reduction already achieved and
the ultimate goal, the frame of reference within which BPT
limitations are established contains neither the prior nor the
subsequent measure.
[
Footnote 15]
EPA defines BPT as
"the average of the best existing performance by plants of
various sizes, ages and unit processes within each industrial
category or subcategory. This average is not based upon a broad
range of plants within an industrial category or subcategory, but
is based upon performance levels achieved by exemplary plants."
39 Fed.Reg. 6580 (1974).
See also EPA, Effluent
Guidelines Div., Development Document for Mineral Mining and
Processing Point Source Category 409 (1979) and Development
Document for Coal Mining 225 (1976). Support for this definition is
found in the legislative history, Leg.Hist. 169-170 (remarks of
Sen. Muskie);
id. at 231 (remarks of Rep. Jones).
[
Footnote 16]
Respondents fail to consider this tension between a general
calculation of costs and benefits and a particularized
consideration of costs when they argue that, because EPA only has
authority to promulgate industry-wide BPT regulations by analogy to
its authority to promulgate industry-wide BAT regulations, the same
kind of economic capability/effluent reduction balancing relevant
to a BAT variance must apply as well to a BPI variance.
[
Footnote 17]
Respondents argue that precluding consideration of economic
capability in determining whether to grant a variance effectively
precludes consideration of the "total costs" for the individual
point source. Respondents rely upon a statement by Representative
Jones as to the meaning of "total cost" in § 304(b)(1)(b):
"internal, or plant, costs sustained by the owner or operator
and those external costs such as potential unemployment,
dislocation and rural area economic development sustained by the
community, area, or region."
Leg.Hist. 231. Unless economic capability is considered, it is
argued, it will be impossible to consider the potential external
costs of meeting a BPT limitation, caused by a plant closing.
Although there is some merit to respondents' contention, we do not
believe it supports the decision of the Court of Appeals. The court
did not hold that economic capability is relevant only if it
discloses "fundamentally different" external costs from those
considered by EPA in establishing the BPT limitation; rather, the
court held that the factors included in § 301(c) must be taken
into consideration. Section 301(c) makes economic capability,
regardless of its effect on external costs, a ground for a
variance. It is this position that we reject.
[
Footnote 18]
Since any variance provision will permit nonuniformity with the
general BPT standard for a given category, we cannot attribute much
weight to those passages in the legislative history, to which EPA
points, that express a desire and expectation that
"each polluter within a category or class of industrial sources
. . . achieve nationally uniform effluent limitations based on
'best practicable' technology no later than July 1, 1977."
"
See Leg.Hist. 162 (statement of Sen. Muskie).
See
also e.g., id. at 170;
id. at 302, 309 (Conference
Report);
id. at 787 (Report of House Committee on Public
Works). Moreover, EPA has itself stated that a variance does not
represent an exception to BPT or BAT limitations, but rather sets
an individualized BPT or BAT limitation for that point source:"
"No discharger . . . may be excused from the Act's requirement
to meet BPT [and] BAT . . . through this variance clause. A
discharger may instead receive an individualized definition of such
a limitation or standard where the nationally prescribed limit is
shown to be more or less stringent than appropriate for the
discharger under the Act."
44 Fed.Reg. 32893 (1979). Therefore, expressions of an intent
that "all" point sources meet BPT standards by 1977 do not
necessarily support EPA's argument.
[
Footnote 19]
U.S. Council on Environmental Quality, Dept. of Commerce, &
EPA, The Economic Impact of Pollution Control (Mar.1972).
See Leg.Hist. 156, 523.
[
Footnote 20]
See also remarks quoted in
n 22,
infra.
[
Footnote 21]
See quotation above.
[
Footnote 22]
Similar remarks were made by Representative Harrington ("No one
in Congress wishes to legislate so irresponsibly that we drive out
of business t.hose who sincerely wish to abide by the new pollution
laws but who, because of a bad state of the economy, will be forced
to close. The $800 million authorized by this section may not be
completely adequate. But it is a start." Leg.Hist. 450).
[
Footnote 23]
Section 507(e) provides in pertinent part:
"The Administrator shall conduct continuing evaluations of
potential loss or shifts of employment which may result from the
issuance of any effluent limitation or order under this chapter,
including, where appropriate, investigating threatened plant
closures or reductions in employment allegedly resulting from such
limitation or order. Any employee who is discharged or laid-off,
threatened with discharge or lay-off . . . because of the alleged
results of any effluent limitation or order issued under this
chapter . . . may request the Administrator to conduct a full
investigation of the matter. . . . [T]he Administrator shall make
findings of fact as to the effect of such effluent limitation or
order on employment and on the alleged discharge, layoff, or
discrimination and shall make such recommendations as he deems
appropriate. Such report, findings, and recommendations shall be
available to the public."
33 U.S.C. § 1367(e).
[
Footnote 24]
See Leg.Hist. 654-659. Representative Abzug emphasized
the first purpose of the provision:
"This amendment will allow the Congress to get a close look at
the effects on employment of legislation such as this, and will
thus place us in a position to consider such remedial legislation
as may be necessary to ameliorate those effects."
Id. at 658. Representative Miller noted that
"some economic hardship, especially in smaller communities who
rely on single, older plants, may result from the requirements of
the pending bill,"
but opposed this provision because he thought that economic
hardships caused by the Act should be addressed systematically by
modifying the Economic Development Act.
Ibid.
[
Footnote 25]
Respondents contend that deference to agency interpretation is
not appropriate in this case, because EPA has not consistently
interpreted the BPT variance requirements. However, in only one
instance has EPA stated that it would consider economic capability
in relation to BPT variance applications. 43 Fed.Reg. 44846-44848
(1978). This was in response to the Court of Appeals decision in
Appalachian Power Co. v. Train, 545 F.2d 1351 (CA4 1976),
and EPA specifically limited this change to steam electric power
generating plants, which were the subject of the court's order.
[
Footnote 26]
This argument appears in
Appalachian Power, supra at
1359, which the Court of Appeals relies upon in
Crushed
Stone. 601 F.2d at 123.
The Court of Appeals also believed that, because there will be
situations in which the BPT and the BAT standards are identical,
see Development Document for Mineral Mining,
supra, n 15, at
438, it would be illogical to allow a variance based on economic
capability for the latter, but not for the former. The result would
be to "close a plant in 1979 which would be allowed to operate
under a variance in 1983." 601 F.2d at 124. This assumes, however,
that a variance would be available even though BPT standards had
not been met, an assumption which EPA rejects, Brief for
Petitioners 27, and which is questionable in light of the
legislative history. Leg.Hist. 232 ("This provision [§ 301(c)]
is not intended to justify modifications which would not represent
an upgrading over the July 1, 1977, requirements of
best
practicable control technology.'" (Rep. Jones, chairman of the
House Conferees)). The suggested contradiction is accordingly
unlikely to appear. In any event, it is of minor significance in
considering the facial validity of the 1977 variance
provisions.
[
Footnote 27]
We find no support for respondents' contention that Congress
implicitly approved the Court of Appeals' reading of the variance
provision, when it considered and passed the 1977 amendments to the
Act. Respondents rely primarily on the discussion of
Appalachian Power in a document prepared by the Library of
Congress for the House Committee on Public Works and
Transportation, Case Law Under the FWPCA Amendments of 1972
(Comm.Print 1977). However, that document notes that there was at
that time a conflict in the United States Courts of Appeals over
the validity of the variance provision, and in no way indicates
that the
Appalachian Power decision was the correct
interpretation.
Id. at 28.