Amicus Curiae Brief — Environmental Defense v. Duke Energy Corporation
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6
Power Company v. Reilly, 893 F.2d 901, 905 (7th Cir. 1990)
(“WEPCO”), United States v. Ohio Edison Co., 276 F. Supp.
2d 829, 862 (S.D. Ohio 2003); United States v. Southern
Indiana Gas and Electric Co., 245 F. Supp. 2d 994, 998
(S.D. Ind. 2003) (““SIGECO”).
In EPA’s PSD enforcement action against Duke
Energy, the Fourth Circuit’s role is to apply the “modifica-
tion” test specified in EPA’s PSD regulations and deter-
mine if the company’s plant renovations triggered PSD
requirements. Yet, completely disregarding section 307’s
clear requirements, the Fourth Circuit announced that
“the language and various interpretations of the PSD
regulations, on which the district court partially based its
holding and which the parties exhaustively discuss, are
largely irrelevant to the proper analysis of this case.”
United States v. Duke Energy, 411 F.3d 539, 547 n.3 (4th
Cir. 2005). Instead of interpreting and applying EPA's
regulations, the Fourth Circuit focused exclusively on
ascertaining what it thought the statute requires, and
based on that statutory reading, announced that the PSD
program must apply the same test as in the NSPS regula-
tions for determining when a “modification” occurs. See id.
at 550. (“Congress’ decision to create identical statutory
definitions of the term ‘modification’ has affirmatively
mandated that this term be interpreted identically for the
two programs.”). Without making any attempt to explain
how EPA’s PSD regulations could be read to establish an
hourly emissions rate test, the court declared that the PSD
test must turn on hourly emissions because “[n]o one
disputes that prior to enactment of the PSD statute, the
EPA promulgated NSPS regulations that define the term
‘modification’ so that only a project that increases a plant’s
hourly rate of emissions constitutes a ‘modification.’” /d.
at 550 (emphasis in original).
The Fourth Circuit tries to explain away the section
307 requirements by stating that “lolur choice of this
interpretation of the PSD regulations — as required under
the statute — over the EPA's interpretation is not an
invalidation of those regulations.” Jd. at 549 n.7. But the
Fourth Circuit did not interpret the regulations; if it did, it
would have no choice but to conclude that the PSD regula-
tions define modification in terms of whether a physical or
operational change will result in an annual emissions
increase, taking into account increased hours of operation
enabled by the change.’ To the contrary, the Fourth Circuit
ignored the PSD regulations and substituted its own test
based on its reading of the statute — something it has no
jurisdiction to do. See Adamo Wrecking v. United States,
434 U.S. 275, 284 (1978) (The district court is not in
violation of section 307 because it “did not presume to
judge the wisdom of the regulation”). See also WEPCO,
893 F.2d at 914 n.6 (“As a preliminary matter, we note
that WEPCO has not asked us to review the propriety of
the NSPS regulations themselves. Indeed, we have no
such jurisdiction to conduct such an inquiry: 42 U.S.C.
section 7607(b\(1) reserves such questions for the [DC
Circuit].... WEPCO simply requests that we consider
whether the EPA properly applied these regulations to the
... generating units. We have jurisdiction to undertake
such an inquiry.”); United States v. Ho, 311 F.3d 589, 607
(5th Cir. 2002); Puerto Rican Cement Co. v. Environmental
Protection Agency, 889 F.2d 292, 299 (1st Cir. 1989).
* See infra pp. 14-15 for further discussion of the plain language of
the PSD regulations.
8
Duke is well aware that a challenge to the validity of
nationally applicable regulations must occur in the D.C.
Circuit; indeed, a host of industry petitioners, including
Duke, challenged various provisions of the 1980 regula-
tions directly in the D.C. Circuit shortly after those regu-
lations were promulgated. See Chemical Manufacturers
Ass’n v. Environmental Protection Agency, Nos. 79-1112 et
al. That case was stayed several times and was recently
revived and consolidated with additional challenges to
EPA’s 2002 rules in New York I. 413 F.3d at 3. In New York
I, after stating that the “Industry petitioners also chal-
lenge the 1980 rule’s definition of modification in the NSR*
context to the extent that it differs from the NSPS defini-
tion,” the court held, “[wje are not convinced.” Jd. at 18.
The D.C. Circuit found no indication in the statute or
legislative history that Congress intended to incorporate
the definition of “modification” in the NSPS regulations
into the PSD program. /d. at 19. Further, the court noted
that the NSPS regulations in place as of the 1977 Act
amendments “used two different (and possibly inconsis-
tent) definitions of modification,” and that “[gliven the two
quite differently worded regulatory definitions of ‘modifi-
cation’ within the NSPS program at the time of the 1977
amendments, it would take a rather pointed indication
from Congress to support the idea that it expressly
adopted one of them for NSR. No such indication exists.”
* NSR or New Source Review is the overarching program that
includes PSD review, for areas in attainment with the National
Ambient Air Quality Standards (“NAAQS”), and Nonattainment New
Source Review, for areas that are not in attainment with the NAAQS.
This case concerns only PSD as the areas where Duke's plants are
located are in attainment for the NAAQS.
* In New York I, the D.C. Circuit rejected industry’s congressional
incorporation argument — that when Congress amended the Clean Air
(Continued on following page)
9
Id. at 19-20 (emphasis in original). In sum, :ust as directed
by section 307, Duke challenged the validity of EPA’s PSD
regulations in the D.C. Circuit. After failing in that chal-
lenge, Duke cannot have a second bite at the apple in this
case.
B. Uniform Judicial Review of Nationally
Applicable Regulations Is Critical to
EPA’s Ability to Properly Carry Out the
Directives of the Clean Air Act.
This case provides a prime example for why assurance
that “the substantive provisions of ... {regulations are]
uniformly applied and interpreted and that the circum-
stances of ... adoption [should] be quickly reviewed by a
single court” is of critical importance to EPA's ability to
implement the Act. Adamo Wrecking, 434 U.S. at 284;
United States v. Ethyl Corp., 761 F.2d 1153, 1156 n.7, 1157
(5th Cir. 1985). Following the enactment of the Clean Air
Act in 1970, EPA was tasked with establishing National
Ambient Air Quality Standards (“NAAQS”), by “iden-
tify{ing] the maximum airborne concentration of a pollut-
ant that the public health can tolerate, decreas[ing] the
concentration to provide an ‘adequate’ margin of safety,
and set(ting] the standard at that level.” Whitman v.
American Trucking Ass’ns, 531 U.S. 457, 465 (2001). The
Act in 1977 and added the PSD program Congress intended to incorpo-
rate the existing NSPS regulations into the PSD program. 413 F.3d at
20. As to the slightly different argument Duke attempts to make here,
the court stated “[wje express no opinion as to whether Congress
intended to require that EPA use identical regulatory definitions of
modification across the NSPS and NSR programs. That argument was
not made by industry petitioners in their opening brief and is therefore
waived.” /d. (internal citations omitted).
10
PSD program is crucial to the Act because it “[s]eek[s} to
prevent backsliding in regions whose air quality [meets
the] NAAQS [by requiring] sources undertaking modifica-
tions to obtain preconstruction permits.” New York I, 413
F.3d at 12. Without uniform, national regulations for the
PSD program, EPA’s ability to approve state implementa-
tion plans (“SIPs”), to write permits and to bring appropri-
ate enforcement actions will be significantly disrupted.
First, the stability and effectiveness of SIPs — which
lie at the core of delegated state enforcement actions —
would be undermined if the Fourth Circuit’s decision is
allowed to stand. The Act requires EPA to approve SIPs,
designed by and for each individual state, provided that
the SIPs “include a program to provide for the . . . regula-
tion of the modification and construction of any stationary
source within the areas covered by the plan as necessary
to assure that the national ambient air quality standards
are achieved, including a permit program.” 42 U.S.C.
§ 7410(a)(2)(C). If the lower courts can invalidate the PSD
regulations at any time, thereby potentially forcing EPA to
redraft the regulations time and again, EPA (and the
states’) could never be certain that the SIPs will actually
contain the appropriate requirements to limit emissions
and achieve the NAAQS. The states would, in essence, be
required to revisit and revise the SIPs every time the
regulations were invalidated and rewritten. 40 C.FR.
§$§ 51.166(a)(3), (4). Since development and adoption of the
regulations is an incredibly costly and time consuming
endeavor, the SIPs would likely be left in limbo for lengthy
* See State of New Jersey’s amicus brief for further discussion of
the importance of uniform PSD regulations in conjunction with the
states’ ability to formulate adequate SIPs.
11
periods of time.’ Section 307 was added to the Act precisely
to prevent such an inefficient scenario. See Adamo Wreck-
ing, 434 U.S. at 284. See also Lubrizol Corp., 547 F.2d at
315, 317.
In addition, without uniform and final PSD regula-
tions, the preconstruction permits will be written under a
veil of uncertainty for both EPA and industry. The PSD
program was established “to assure that any decision to
permit increased air pollution in any area... is made only
after careful evaluation of all the consequences of such a
decision.” 42 U.S.C. § 7470(5). To carry out this goal, the
Act provides that “[n]o major emitting facility ... may be
constructed [or modified] in an area |that has attained the
NAAQS] unless ... the required analysis has been con-
ducted in accordance with regulations promulgated by the
Administrator.” 42 U.S.C. §§ 7475(a\(2), 7479(2\(c). Such
regulations must “assurle] that maximum allowable
increases ... [of pollutants] shall not be exceeded.” 42
U.S.C. § 7473(a). EPA and the states, when issuing per-
mits, bear the responsibility of ensuring that modifications
to existing sources do not “cause, or contribute to, air
pollution in excess of” these thresholds. 42 U.S.C.
§ 7475(aX(3).
" For example, when the 1978 PSD regulations were successfully
challenged in Alabama Power under section 307 in the D.C. Circuit, it
took EPA two years (until August, 1980) to issue amended regulations.
See Alabama Power Co. v. Costle, 636 F.2d 323 (D.C. Cir. 1980). See also
43 Fed. Reg. 26,380 (June 19, 1978); 45 Fed. Reg. 52,676 (Aug. 7, 1980).
When EPA's 1997 rules for ozone NAAQS were successfully challenged
under section 307 in the D.C. Circuit (and then appealed to this Court),
it took EPA seven years (until April, 2004) to issue amended regula-
tions. See American Trucking Ass’ns, 531 U.S. 457. See also 62 Fed.
Reg. 38,856 (July 18, 1997); 69 Fed. Reg. 23,951 (April 30, 2004).
12
The potential for changing regulations would create
competitive disparity across industry if some facilities are
permitted under old regulations, while others are permit-
ted under new regulations.” EPA should not be tasked with
the prospect of redrafting industry permits throughout the
life of the regulations in response to industry challenges to
the regulations. Such a scenario will provide incentive for
regulated entities to challenge regulations any time they -
are unhappy with their permit or are targeted in an
enforcement action. Although EPA is certainly able to
revisit regulations on its own, due to changed circum-
stance or otherwise, any revisions to the regulations would
be subject to notice and comment rulemaking, not the
unilateral decision of a lower court judge.
Finally, the Clean Air Act’s enforcement scheme would
break down in the face of an affirmation of the Fourth -
Circuit’s decision. “The process [for completing a new
source review case] can take years due to: the size of
utilities; the amount and complexity of historical informa-
tion involved; the type of utility expertise needed to
effectively develop an NSR case; and the limited EPA,
State, and local agency enforcement resources.” New
Source Review Rule Change Harms EPA's Ability to En-
force Against Coal-fired Electric Utilities, Office of Inspec-
tor General, Report No. 2004-P-00034, Sept. 30, 2004, pp.
22-23 (available at http://www.epa.gov/oig/reports/2004/
20040930-2004-P-00034.pdf). See also Air Pollution: EPA
Should Improve Oversight of Emissions Reporting at Large
* EPA believes that the Fourth Circuit’s “holding creates a poten-
tial disparity in the way we interpret the program in States in the
Fourth Circuit compared to States in other Circuits in the country.” 70
Fed. Reg. 61,081, 61,083 (Oct. 20, 2005).
13
Facilities, Government Accounting Office, April 2001, pp.
10-11 (available at http://www.gao.gov/new.items/d0146.
pdf). EPA will usually begin by submitting a section 114
request for documents to the regulated entity and can
spend years reviewing these documents before attempting
settlement, filing its own administrative complaint or
referring the case to the Department of Justice for en-
forcement. See id. See also 42 U.S.C. § 7413(a\(1); 42
U.S.C. § 7414. Discovery in this case alone “produced
approximately 46 million pages of documents ... {and}
lengthy briefs [were] accompanied by thousands of pages
of exhibits.” United States v. Duke Energy, 278 F. Supp. 2d
619, 622 (M.D.N.C. 2003). If EPA has to change course in
the middle of building an enforcement case in response to
the invalidation of its own regulations, enforcement
actions will become overwhelmingly inefficient, and in
some circumstances enforcement will simply fall away.
Such a scenario is not what Congress envisioned when the
Clean Air Act was enacted.
II. EVEN IF THE FOURTH CIRCUIT HAD JURIS-
DICTION, ITS REGULATORY INTERPRETATION
DISREGARDS THE PLAIN LANGUAGE OF THE
PSD REGULATIONS AND VIOLATES THE ACT.
industry’s hourly emissions test for triggering PSD
requirements is contrary to the purposes of the Act, EPA’s
consistent PSD regulations, and related case law. The
plain language of the PSD regulations clearly provide for
an actual annual emissions test taking into account
increased hours of operation enabled by a change at a
facility. In addition, only an annual emissions test will
fulfill the purposes of the PSD program to prevent back-
sliding in regions where the air quality is adequate. And
14
the fact that industry, including Duke, and EPA entered
into a settlement agreement that required EPA to propose
an hourly test after the applicable 1980 PSD regulations
were finalized provides further proof that an hourly test
does not apply to this case. Since an hourly test does not
capture total actual annual emissions increases from a
source, such a test simply cannot be sanctioned.
A. Industry’s Hourly Test Is Contrary to the
Plain Language of EPA’s PSD Regulations.
Contrary to the Fourth Circuit’s decision, EPA’s PSD
regulations unmistakably require an annual test, not an
hourly test, for calculating an emissions increase that will
trigger the PSD permitting requirements. The Act requires
the owner or operator of a major stationary source to
obtain a permit before undertaking a “modification,” which
the Act defines as “any physical change in, or change in
the method of operation of, a stationary source which
increases the amount of any air pollutant emitted by such
source or which results in the emission of any air pollutant
not previously emitted.” 42 U.S.C. §7411l(a\4). The
regulations clarify that PSD requirements are triggered
only for “major” modifications. 40 C.F.R. § 51.166(i2). A
major modification occurs where a “physical change ...
would result in a significant net emissions increase.” 40
C.F.R. § 51.166(b\2\i). A significant net emissions in-
crease can be broken into a four-part test:
1. Emissions increase: “[a}ny increase in actual
emissions from a particular physical change or
change in the method of operation at a stationary
source.” 40 C.F.R. § 51.166(b\3)iXa) (emphasis
added).
15
2. Actual emissions: “the actual rate of emis-
sions of a pollutant from an emissions unit .. . In
general, actual emissions as of a particular date
shall equal the average rate, in tons per year, at
which the unit actually emitted the pollutant
during a two-year period which precedes the par-
ticular date and which is representative of nor-
mal source operation. ... Actual emissions shall
be calculated using the unit’s actual operating
hours, production rates, and types of materials
processed, stored, or combusted during the select
time period.” 40 C.F.R. §51.166(b)\21)i), Ui)
(emphasis added).
3. Netting: combine step two with: “|a|ny other
increases and decreases in actual emissions at
the source that are contemporaneous with the
particular change and are otherwise creditable.”
40 C.F_R. § 51.166(b)(3)(b).
4. Significant: The net emissions increase must
exceed pollutant specific annual emissions
thresholds expressed in tons per vear. For exam-
ple, the net emissions increase for sulfur dioxide
must exceed 40 tons per year to trigger the PSD
requirements. 40 C.F.R. § 51.166(b)(23)(1).
The lower courts’ interpretation of this regulatory
language as warranting an hourly emissions test is com-
pletely unfounded. The words “hourly emissions” exist
nowhere in the text of the regulations. Thus, it is unsur-
prising that the Fourth Circuit’s decision omits any
explanation for how the regulations could be read to
establish an hourly test. In light of the plain regulatory
language establishing an actual annual emissions test for
determining PSD applicability, the Fourth Circuit's con-
clusion that EPA must apply an hourly test should be
rejected.
16
B. The EPA Regulations and Related Case Law
Regarding PSD Confirm that Duke Was Re-
quired to Consider Increased Emissions
Caused by Increased Hours of Operation
When Evaluating Whether PSD Requirements
Applied to its Plant Renovations.
The “net emissions increase” step of the “major modi-
fication” test clearly requires a comparison of the pre- and
post-project annual emissions, including “actual operating
hours.” 40 C.F.R. § 51.166(b)(21)(ii). The lower courts’
determination that the pre-project hours of operation must
remain constant in calculating the emissions increase is
simply incorrect. See Duke Energy, 411 F.3d at 545, Duke
Energy, 278 F. Supp. 2d at 640. The so-called “hours of
operation exclusion,” which states that “[a] physical
change ... shall not include ... [a]n increase in hours of
operation,” does not apply to this case. See 40 C.F.R.
§ 51.166(b)(2 iii). Rather, this exclusion simply clarifies
that a facility that is not operating at capacity may in-
crease its hours of operation “to take advantage of favor-
able market conditions,” 45 Fed. Reg. 52,676, 52,704 (Aug.
7, 1980), without triggering PSD requirements, as long as
this increase is achieved without an associated “physical
change in or change in the method of operation of,” 40
C.F.R. § 51.166(b)2)i), the source. In other words, an
increase in hours of operation, on its own, does not consti-
tute an NSR-triggering physical or operational change.
The exclusion does not apply to the present case because
the increase in hours of operation occurred as a result of
the physical changes that Duke made to its facilities.
EPA and the courts have consistently interpreted the
exclusion in this manner. EPA confirmed the narrow
application of the hours of operation exclusion when it
17
issued the applicability determination for the proposed
modifications at the WEPCO plants. WEPCO argued that
since “any emissions increases would be due to increased
production rates or hours of operation rather than higher
emissions per unit of production.... these increases
should be excluded from consideration in determining
whether a net significant emissions increase and, hence, a
major modification, would occur.” Applicability of Preven-
tion of Significant Deterioration Requirements (PSD) and
New Source Performance Standards (NSPS) Requirements
to the Wisconsin Electric Power Company (WEPCO) Port
Washington Life Extension Project, Memorandum From:
Don R. Clay, Acting Asst. Admin. For Air and Radiation,
To: David A. Kee, Director, Air and Radiation Division,
Region V, Sept. 9, 1988, p. 8 (Joint Appendix “JA” 257-58).
EPA responded to WEPCO’s argument by stating that:
The WEPCO is incorrect in this regard.... the
exclusions cited by WEPCO are intended to apply
where a source increases emissions by simply
combusting a larger amount of fuel, or processing
a larger amount of raw materials during a given
time period, or by expanding its hours of opera-
tion ‘to take advantage of favorable market con-
ditions’ (see 45 FR 52704) ... it is obvious that
WEPCO’s plans to increase production rate or
hours of operation are inextricably intertwined
with the physical changes planned under the life
extension project... . [A]ccepting WEPCO’s inter-
pretation of the major modification regulations
would serve to exclude from consideration all
physical or operational changes except those which
cause increased emissions per unit of production.
Clearly, EPA never intended this result. It would
allow, through substantial capital investment,
significant expansion of the pollution-emitting
18
capacity and longevity of major industrial facili-
ties without PSD review of the impacts on air
quality.
Id. (emphasis added).
In a follow up letter to the Vice President of WEPCO,
EPA staff again confirmed the narrow application of the
exclusion by stating that “an increase in any one of these
three factors [emission rate, production rate or capacity
utilization, and hours of operation], if attributable to a
physical or operational change, can trigger an emissions
increase for PSD purposes .. . EPA explicitly assumed that
emissions increases ... would come ... from increases in
production rate or hours of operation.... The hourly
capacity demonstration for NSPS purposes is not relevant
to the PSD analysis.” Letter From: Don R. Clay, Acting
Asst. Admin. For Air and Radiation, To: John W. Boston,
Vice President of WEPCO, February 15, 1989, pp. 9-10 (JA
294-95). EPA’s applicability determination in regard to the
hours of operation exclusion was ultimately confirmed by
the Seventh Circuit where the court decided, inter alia,
that “[djespite WEPCO’s protestations, we note initially
that the EPA’s refusal to apply the ‘production rate/hours
of operation exclusion’ was proper. This exclusion ... was
provided to allow facilities to take advantage of fluctuating
market conditions, not construction or modification activ-
ity.” WEPCO, 893 F.2d at 916 n.11 (internal citations
omitted) (emphasis added). See also Puerto Rican Cement,
889 F.2d at 298.
This application of the exclusion was again memorial-
ized in the preambles to EPA’s 1992 and 2002 rules: “Al-
though a source may vary its hours of operation or
production as part of its everyday operations, an increase in
emissions attributable to an increase in hours of operation or
19
production rate which is the result of a construction-
related activity is not excluded from review.” 57 Fed. Reg.
32,314, 32,328 (July 21, 1992). “|A]n increase in utilization
should not trigger the major NSR requirements unless it is
related to a physical or operational change. .. . [T]he CAA
only applies the major NSR requirements to emissions
increases that are the result of a physical or operational
change. Thus, we do not believe that the major NSR
requirements should apply to a utilization increase unless
the increase is related to the modification.” 67 Fed. Reg.
80,186, 80,203 (Dec. 31, 2002).
Failing to cite a single EPA regulation or judicial
decision in support of its broad-based interpretation of the
hours of operation exclusion, Duke relies solely on an
internal EPA memorandum and a ietter written by a
single EPA staff member in the early 1980s. See Memo-
randum From: Edward E. Reich, Director Division of
Stationary Source Enforcement, To: Charles Whitmore,
Chief, Technical Analysis Section, Region VII, Jan. 22,
1981 (JA 35-37). See also Letter From: Edward E. Reich,
To: Amasjit S. Gill, General Electric, June 24, 1981 (JA 27-
28). Given that the consistent EPA documents (discussed
above) were written both before and after the conflicting
memorandum and letter, as the court in Puerto Rican
Cement similarly held, “these materials do not show a
significant, legally recognizable ‘conflict’ within the
agency.” 889 F.2d at 299. The Fourth Circuit cannot simply
retract the plain language of the regulations and EPA's
and the courts’ historically consistent, narrow application
of the exclusion based on one EPA staff member’s misstep.
See id. See also Ohio Edison Co., 276 F. Supp. 2d at 876-77
(rejecting reliance on Reich letters for same proposition).
Indeed, because “(t]he purpose of the ‘consistency’ doctrine
20
in administrative law is . . . to prevent the agency . . . from
significantly changing those policies without conscious
awareness of, and consideration of the need for, change,”
such a deviation in the application of the regulations
would require EPA to undergo notice and comment rule-
making.’ Jd. The lower courts’ reliance on these documents
for applying the hours of operation exclusion to the pre-
sent facts, and the resulting hourly emissions test, is
therefore improper.
Since EPA and the courts have repeatedly and consis-
tently described the appropriate application of the hours of
operation exclusion, this narrow application should come
as no surprise to Duke. As the Southern District of Indi-
ana court explained in a similar PSD enforcement case,
Congress sweepingly defined modification . . . [for
PSD purposes], and the goal of the CAA was ‘to
speed up and intensify’ the war against pollution.
Moreover, the D.C. Circuit rejected the EPA’s ear-
lier attempts to make broad, categorical exclu-
sions from the CAA’s definition of modification.
Sez Ala. Power v. Costle, 204 U.S. App. D.C. 51,
636 F.2d 323 (D.C.Cir.1979) []. With this regula-
tory context in mind, a context that a sophisti-
cated entity like SIGECO [or in this case Duke]
was surely aware of, it would be inconsistent for
the EPA to broadly define a regulatory exemption
(for PSD].
SIGECO, 245 F. Supp. 2d at 1014.
* In fact, EPA is currently taking comments on a proposed rule for
an hourly emissions test for PSD. 70 Fed. Reg. 61,081 (Oct. 20, 2005).
See infra, pp. 26-27. Therefore, EPA recognized that notice and com-
ment rulemaking was necessary if such a departure is going to occur.
21
In sum, there is no merit to the Fourth Circuit’s
conclusion that EPA’s PSD regulations authorize sources
to exclude emissions resulting from increased hours of
operation made possible by a physical change when
assessing whether that change triggers PSD review. Here,
Duke’s massive renovations plainly enabled its plants to
increase their hours of operation, dramatically increasing
the actual amount of pollution they release into the air
each year. By discounting those emission increases and
proceeding without PSD review, Duke violated the Act.
C. An Hourly Emissions Rate Test for PSD Would
Undermine the Purposes of the Act’s PSD Pro-
visions.
The NSPS and PSD programs were added to the Act
at different times and serve different purposes. In 1970,
Congress included the NSPS program in the Act and EPA
was then required to promulgate technology-based emis-
sion limits for categories of sources without regard to site-
specific factors. 42 U.S.C. § 7411(a)(1). In 1977, when the
Act was amended, Congress added the PSD program to,
inter alia, prevent the quality of the air from deteriorating
in areas that are in attainment with the NAAQS. 42
U.S.C. § 7470. The NSPS program is based solely on the
particular type of equipment or facility emitting the
pollutants, whereas the PSD program establishes control
requirements on a case-by-case basis taking into account
site-specific factors such as the specific environmental
impact a new or modified source will have upon the area
where it will be located. See 57 Fed. Reg. 32,314, 32,315-
316 (July 21, 1992). See also Northern Plains Resource
Council, 645 F.2d at 1356. EPA reinforced these differences
by promulgating different tests for triggering PSD and
22
NSPS requirements: “In contrast [to the NSPS hourly
emissions rate test and] in light of the air quality planning
component of the NSR program, the NSR regulations
examine total actual annual emissions to the atmosphere.
Consequently, normal operations over a period of time is
considered for purposes of determining a source’s impact
on ambient air.” 57 Fed. Reg. at 32,331. Only an annual
emissions test will fulfill the purpose of the PSD program
to prevent backsliding in regions where the air quality is
adequate.
To prevent facilities from significantly deteriorating
the air quality, PSD statutory and regulatory provisions, in
conjunction with the SIPs, establish and assure compliance
with “increments” or “maximum allowable increases” of
pollutants. 42 U.S.C. § 7475(a), (d), 7473(a), (b); 40 C.FR.
§ 51.166(c). An owner or operator of a facility seeking to make
modifications must demonstrate that “emissions from con-
struction or operation of such facility will not cause, or con-
tribute to, air pollution in excess of” these increments. 42
U.S.C. § 7475(a\(3). The PSD permitting process is the mecha-
nism under which EPA examines appropriate consumption of
these increments. 42 U.S.C. § 7475(a)(2). Since an hourly test
does not capture the total actual emissions increases result-
ing from a change, EPA will not be able to accurately quan-
tify adverse impacts on air quality when doling out
preconstruction permits in PSD areas. The preamble to
EPA's 1980 regulations supports this analysis:
Source applicants ... must ... perform an analysis
to compute how much of the PSD increment re-
mains available to them. In general the amount of
increment that is available depends on certain
changes in actual emissions.... Accordingly,
cleanup adds to the available growth margin while
23
new emissions diminish it. ... Once the question
of how much increment remains is resolved, then
the applicant must demonstrate that his pro-
posed new emissions would not exceed the re-
maining PSD increment. Where a_ proposed
project would cause a new violation of the incre-
ment or contribute to an existing violation, it
cannot be approved. Existing violations must be
entirely corrected before PSD sources which af-
fect the area can be approved.
45 Fed. Reg. 52,676, 52,678 (Aug. 7, 1980).
Recognizing that not all emissions increases should
trigger the PSD requirements, EPA established “signifi-
cant net emissions increase” thresholds calculated in “tons
per year.”” 40 C.F.R. § 51.166(b)(23)i) (emphasis added).
Before establishing these thresholds, EPA analyzed the
“cumulative effect on increment consumption of multiple
sources in an area each making the maximum de minimis
emissions increase (thereby going unreviewed under PSD
at the time of the change).” 45 Fed. Reg. 52,676, 52,707
(Aug. 7, 1980). EPA understood that if too many unac-
counted for insignificant modifications occurred, EPA
would not be able to enforce the emission increments
through the PSD permitting requirements. Yet, this is
exactly what will happen if the Fourth Circuit’s hourly test
is sanctioned. Projects that do not increase hourly emis-
sions but do significantly increase hours of operation, and,
in turn, annual emissions, would escape PSD review.
Unless EPA is able to consider actual annual emissions
increases, including emissions resulting from increases in
These significance thresholds are the fourth step in the “major
modification” definition. See supra p. 15.
24
hours of operation, the emissions inventory will be se-
verely disrupted, and the PSD program will not function
properly.
D. Industry, Including Duke, Was Well Aware
that the Test for PSD Was Annual Emis-
sions, Not Hourly Emissions.
Following industry’s initial challenge to the 1980 PSD
regulations, a settlement agreement ensued, whereby EPA
agreed to propose a regulatory amendment that would
allow sources to “calculate emissions ... based on either
the actual emissions methodology in the existing rules or
the unit’s potential emissions, measured in terms of hourly
emissions.” 61 Fed. Reg. 38,250, 38,268 (July 23, 1996)
(discussing and proposing language from 1982 Settlement
Agreement). In other words, by entering into this settle-
ment agreement, EPA and industry effectively agreed that
the 1980 rules already included projects that increase
actual annual emissions but do not increase potential
hourly emissions and that EPA would propose and take
public comment on an amendment to exclude such pro-
jects. If industry believed that such projects were already
excluded from the 1980 PSD regulations, as they allege in
th.: case, then there would be no incentive for industry,
including Duke, to settle in 1982 based on EPA's agree-
ment to propose their desired test for public comment.
In 1996, EPA proposed for public comment the lan-
guage agreed to in the 1982 Settlement Agreement:
“sources may calculate emissions increases and decreases
... Measured in terms of hourly emissions (i.e., pounds of
pollutant per hour).” 61 Fed. Reg. at 38,268. EPA noted
that “[t)he primary effect of an hourly potential test is to
eliminate a source's level of operations as a factor when
25
determining whether a proposed change will result in an
increase. Past and future level of utilization of the source
are completely disregarded.” Jd. at 38,269. After a prelimi-
nary analysis of the proposed rule, EPA concluded that:
[T]here is concern for the environmental conse-
quences. For example, assume the emissions unit
at the widget factory that is emitting 10 pounds
an hour but has historically operated at 40 per-
cent capacity due at first to operating cost, but
with age, reduced efficiency and reliability. Un-
der the [hourly potential test], the owner could
modernize the unit ... [and] allow the owner to
use the machine at much higher levels (e.g., more
hours per day or week) than it had in the past.
As a result actual emissions (measured in tpy
- [tons per year]) could more than double due to
the increase in utilization even though hourly po-
tential emissions remain the same.... [O]ne of
the most troubling side effects of the . . . proposal
is that it could ultimately stymie major new
source growth by allowing unreviewed increases
of emissions from modifications of existing
sources to consume all available increment in
PSD areas.... (U)nder the ... [proposal] an old
grandfathered source could experience a ‘signifi-
cant’ net increase in annual actual emissions, yet
it would not necessarily be subject to review.
Id. at 38,269, 38,270.
In 2002, after receiving comments on the hourly
emissions test for triggering PSD review, EPA rejected the
test. 67 Fed. Reg. 80,186, 80,205 (Dec. 31, 2002). EPA
reasoned that an hourly test
26
could sanction greater actual emissions increases
to the environment ... without any preconstruc-
tion review. In addition, actual emissions increases
resulting from unreviewed projects could go largely
undocumented until a PSD review is performed by
a new or modified facility that ultimately must un-
dergo review. By that time, however, a violation of
an increment could have unknowingly occurred. .. .
We agree that ... [the proposed hourly test] could
lead to unreviewed increases in emissions that
would be detrimental to air quality and could make
it difficult to implement the statutory require-
ments for state-of-the-art controls.
Id.
Although EPA's latest proposed PSD regulations depart
from the lengthy historic consistency described above, it only
further illustrates that the regulations applicable in this case
provide for an actual annual emissions test. In October, 2005,
EPA requested public comment on amendments to the PSD
program that would allow existing power plants, such as
Duke’s, “to use the same maximum achievable hourly |
emissions test we apply under NSPS to determine whether a
physical change in or change in the method of operation .. .
results in an emissions increase.” 70 Fed. Reg. 61,081, 61,088
(Oct. 20, 2005). Indeed, EPA states in the 2005 proposed rule
that “EPA entered into a Settlement Agreement which
required us to propose an NSPS-like, hourly-potential-to-
hourly-potential emissions increase test for modification,”
and that the current PSD rules require “a source [to] look{]
at whether a project will result in a significant emissions
increase on an annual basis.” Jd. EPA asks for comment on
this proposed rule a minimum of 25 times in the 22-page
document; EPA recognizes that the proposed rule is a
27
stark departure from the previous long-standing actual
annual emissions test.”
EPA’s use of an actual annual emissions test, rather
than an hourly potential test, should come as absolutely no
surprise to Duke. EPA was quite capable of writing an hourly
emissions test if it so desired, as it plainly did for the NSPS
program 30 years ago and as it has only now proposed for the
PSD program. If industry and EPA believed that an hourly
rather than annual test already existed, the 1982 settlement,
the resulting 1996 proposal, the 2002 rejection of that
proposal, and the subsequent 2005 proposal would not be
necessary.
e
CONCLUSION
The decision of the Fourth Circuit Court of Appeals
should be reversed in its entirety.
Dated: July 21, 2006
Respectfully submitted,
HOLLY D. GORDON*
DEBORAH A. SIVAS
STANFORD LAW SCHOOL
ENVIRONMENTAL LAW CLINIC
Crown Quadrangle
559 Nathan Abbott Way
Stanford, California 94305-8610
Telephone: (650) 725-8571
Facsimile: (650) 723-4426
*Counsel of Record
“ The 2005 proposal clearly states that “|t}he proposed rule would
only apply prospectively.” 70 Fed. Reg. at 61,081 (Uct. 20, 2005).
This is a copy of a public record, reproduced as it was published. It is not legal advice, and it may not be the version a court would rely on. Check the official source before you cite it.