Amicus Curiae Brief — Environmental Defense v. Duke Energy Corporation
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FILED
gy SEP 15 2006
No. 05-848 | SGPweme EME COUR cate )
In the
Supreme Court of the Anited States
¢
ENVIRONMENTAL DEFENSE, ET AL.,
Petitioners,
Vv.
DUKE ENERGY CORPORATION, ET AL.,
Respondents.
’
On Writ of Certiorari to the
United States Court of Appeals
for the Fourth Circuit
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BRIEF OF THE STATES OF ALABAMA, ALASKA,
COLORADO, INDIANA, KANSAS, NEBRASKA,
SOUTH CAROLINA, SOUTH DAKOTA, VIRGINIA, AND
WYOMING, AND THE STATE OF WEST VIRGINIA
DEPARTMENT OF ENVIRONMENTAL PROTECTION, AS
AMICI CURIAE IN SUPPORT OF RESPONDENTS
SJ
Olivia Rowell Troy King
General Counsel Attorney General
ALABAMA DEPARTMENT OF Kevin C. Newsom
ENVIRONMENTAL MANAGEMENT Solicitor General
1400 Coliseum Blvd. Counsel of Record”
Montgomery, Alabama 36110
(334) 271-7858 Robert D. Tambling
Chief, Environmental Division
STATE OF ALABAMA
Office of the Attorney General
11 South Union Street
Montgomery, Alabama 36130
September 15, 2006 (334) 242-7401
(Additional counsel for amici curiae are listed inside the front cover.)
a nee ee en ne a eae en
ADDITIONAL COUNSEL
DAVID W. MAi.QUEZ
ATTORNEY GENERAL
STATE OF ALASKA
P.O. Box 110300
~ Juneau, AK 99811
JOHN W. SUTHERS
ATTORNEY GENERAL
STATE OF COLORADO
1525 Sherman Street
5th Floor
Denver, CO 80203
STEVE CARTER
ATTORNEY GENERAL
STATE OF INDIANA
302 W. Washington Street
Indianapolis, IN 60601
\ PHILL KLINE
ATTORNEY GENERAL
STATE OF KANSAS
120 S.W. 10th Avenue
Topeka, KS 66612-1597
JON BRUNING
ATTORNEY GENERAL
STATE OF NEBRASKA
2115 State Capitol
Lincoln, NE 68509-8920
HENRY D. MCMASTER
ATTORNEY GENERAL
STATE OF SOUTH
CAROLINA
P.O. Box 11549
Columbia, SC 29211
LAWRENCE E. LONG
ATTORNEY GENERAL
STATE OF SOUTH DAKOTA
1302 E. Highway 14
Suite 1
Pierre, SD 57501-8501
ROBERT F. MCDONNELL
ATTORNEY GENERAL
COMMONWEALTH OF
VIRGINIA
900 EAST MAIN STREET
RICHMOND, VA 23219
PATRICK J. CRANK
ATTORNEY GENERAL
STATE OF WYOMING
123 State Capitol
Cheyenne, WY 82002
STEPHANIE R.
TIMMERMEYER
CABINET SECRETARY
STATE OF WEST VIRGINIA
DEPARTMENT OF ENVI-
RONMENTAL PROTECTION
601 57th Street
Charleston, WV 25304
QUESTIONS PRESENTED
1. Whether the Clean Air Act’s provision for expedited
judicial review of “final action” promulgated by EPA, 42
U.S.C. §7607(b), stripped the courts below of authority to
consider a new interpretation of EPA’s 1980 New Source
Review rules that was developed and imposed in an en-
forcement action initiated in 1999; and
2. Whether EPA unlawfully interpreted its New Source
Review rules to convert existing electric generating plants
into “new sources,” even though those plants had not
undergone “modifications” as that term has been defined
and used for decades under those rules and under the Act.
TABLE OF CONTENTS
SEOs CIEE ND cecsecsccesscncvssespesoscmssveneesssnentusneernasinciote i
CE FT EINE BD scicicesenceestecciciidnientinceamneainnteantattiont iv
| + SR oe re NN 1
SUMMARY OF THE ARGUMENT.............s:scsccssssssseeseesneneneeees 1
IL EPA’s Current Litigating Position Is Not
Entitled to Deference, Particularly Given EPA’s
Consistent Endorsement of State Agencies’
Longstanding PSD Interpretations to the
Ci ictinescintnsnstnecpensintgsdunintitossiniliaintinctnindsimentincingniniaien 4
A. EPA Has Consistently Blessed State-Agency
PSD Interpretations Contrary to the One It
FOUUE POIRIER, picstescvcscscicennesintncapiteneinanintmnanincnesoeensees S)
B. EPA’s Own Pronouncements Concerning
the PSD Rule Have Been Frightfully
BRD UIIIIIIIINE, ccc cccnsseceosionsqcapetaptansivaneancemeanniemignmesnmesces 10
Il. EPA’s Litigating Position Undermines the
Clean Air Act's Carefully Calibrated State-
Federal Enforcement Scheme............:csssssssssessesesesnsnseesseees 14
A. Under EPA’s Litigating Position, the
Exception of Federal Intervention Would
Swallow the Rule of State Control.............0::seseesserees 15
B. There Is a True Federalism-Respecting
Solution Here: If a State Wants Stricter
New-Source Controls, It Should Simply
RCE TIGR, .cccxccssecsssaresssecscersnesasstesscsepnevesnepnensseseees sone ED
II. EPA's Litigating Position Has No Basis in the
Real-World Practicalities of Clean-Air
ili
IV. EPA’s Litigating Position Has Fundamental
Drawbacks Even as a Matter of Environmental
Ps davicnsencisdanencecnrippesesnnttigniesnniacbantenisnephinteastteaepnecesseats 24
V. Section 307(b) Does Not Preclude Enforcement-
Proceeding Targets From Defending by
Challenging EPA’s. Application of Clean Air
FOE i accrcntinninensinnicciveniacaniesnesiiceninepeaansentsinlanietetanuiecneasiie 28
iv
TABLE OF AUTHORITIES
Cases
Adamo Wrecking Co. v. United States, 434 US. 275
GPR ncnnipssoceesoansanenvesseninrpuatnaneorencsniresninannntariprasinistsennnsiansiyh 30
Alaska Dep't of Envtl. Conservation v. EPA, 540 U.S. 461
IIE) nxcececincactossncvenqescnecssectesspesneniccnnionnseeneeivinanasiitnasetia passim
Alaska Prof! Hunters Ass’n v. FAA, 177 F.3d 1030
CA, Ce, BaD) -nnccersescimnsivinnenieetaitwnseeniascnasnmnavinntniovintetnaisi 13
Bennett v. Spear, 520 U.S. 154 (1997)........scsssssssesssessssesesreneneeees 29
Bowen v. Georgetown Univ. Hosp., 488 U.S. 204 (1988)............ 13
Caruso v. Blockbuster-Sony Music Entertainment Centre
at the Waterfront, 193 F.3d 730 (3d Cir. 1999)........0..00s0000+s 13
Chevron, U.S.A., Inc. v. NRDC, 467 US. 837 (1984)............00-+. 13
Good Samaritan Hosp. v. Shalala, 508 U.S. 402 (1993) ..........0+«. 13
INS v. Cardoza-Fonseca, 480 U.S. 421 (1987)........0---secssescerseres 13
New State Ice Co. v. Liebmann, 285 U.S. 262 (1932)............ 19, 20
New York v. EPA, 443 F.3d 880 (D.C. Cir. 2006)........0.2+0+: 18, 28
North Haven Bd. of Educ. v. Bell, 456 U.S. 512 (1982)...........+++. 13
Paralyzed Veterans of America v. D.C. Arena, 117 F.3d
FFD. e. WOGF) .cccepeesnectaserecetectapivennenitacinagsincinesniesonstiets 13
Rodriguez v. United States, 480 U.S. 522 (1987)......-.-..sesereresenes 26
Train v. NRDC, 421 U.S. 60 (1975)......2-cceceseresererenenssenensess 16,17
Union Elec. Co. v. EPA, 427 U.S. 246 (1976) .......0-vcrerereereeee 16, 20
United States v. Alabama Power Co., 372 F. Supp. 2d
1283 (N.D. Ala. 2005)........---sessessssssssserssnsesssesenessensesnseess 6, 13
United States v. Duke Energy Corp., 278 F. Supp. 2d 619
ETE L,, TRGB) sccccrnccsevnstnesnceensencattonrmemancsinestiasstneatsianens 11,12
v
United States v. Georgia-Pacific Corp., No. 1 96-CV-
1818-FMH (N.D. Ga. July 18, 1996) ...ccescssscesnessneesneene 18
United States v. Lopez, 514 U.S. 549 (1995) ..........sesecsesesrenseeneees 19
Whitman v. American Trucking Ass’ns, 531 U.S. 457
GED cxensevernterennatnssecivaseicandeshmsmnannunasdigutensumnemndnussbemngutenntnteses 29
Wisconsin Elec. Power Co. v. Reilly, 893 F.2d 901 (7th
ae ee arabrerersisnneputetesivaheiennapiecepitmnieranciomncbeipeiaterinnnadaiens 11
Statutes
ie ON ie cininitncernshcseenneininteinienmnpiontgnininennatentneinantte 15
as terete toctncecpemnentennssttesescantenteecznaniovensmnanstensennenien 15
aN orcinctpncnctinincncentiesbsipsanasseiianiniiinininennianenasnibinigtedgesnmaniont 15
See SI cntictripsiceretuinstmnsnansndinincteinsasiininiasstintincschecens 15, 16
eee I arinctinctptocencntinanrprinninibicnecinnntistecimntatncenneeniinne 10
GEREN oe dea era oe 10
aN IE iin chp cheaectotincsiaenenticncsigpbiviatinianpestiontminingnentedtans 16
ne UI tbe etieecntentetpcicinsnsectennieanreecesenemnntnionanchnsuntesenanee 20
ea EP sinidhctncpnlincninipnciennninianntnntntenannnntnajnensinginivanennnsmin 22
SEC Ee 23
ee TE rtrin dips eseriechnsinibedectbinieminlitaeeumbeetehoqnnnntiennh 25
gE sche tochs cicercicnncninnsseceneneiutnipetntncertensbuibintacinnssstetsnags 9
ea cictestncicternprtniicincinpeiatsenatitantinnianiecininngs 17, 25
aes Gr ettecgrepencerenecstncteinnivinercemnasienasstcsniesstanssnnessstes 17
als rth cciniinhnctineninescrnipnnninnecntingmatnsnantticeninnten i, 28
a ee I rerctnceccerestnicncnnesncticunscecntincneentesinctetnscennn 26
a re I cic dectriacnsncennsinchsscpneehssinsiinsnssicnamtincenensioe 26
Mid. Code. Arm. §2-1001 et 569 ............ccsceccsssssesssesssesesenssscensesees 21
vi
N.C. Gen. Stat. §143-215.107D(b)-(d)..............sccesecreenesecneeneneees 20
Regulations
40 C.F.R. §51.166(b)(21) & ()(32) (1993) 020... ececsecseeneneenennees 12
SK, Fi I ccccrtrrenseeenntntipncteinnirnseer. cantguincmtpinsiiols 7
45 Fed. Reg. 52,676 (Aug. 7, 1980) (codified at 40
oe, eT 4
46 Fed. Reg. 55,517 (Dec. 10, 1981) (codified at 40
i ED crcenisstnnpnicnencitensccnntenpsqnccecicentesientivivintiet 5-6
47 Fed. Reg. 6017 (Feb. 10, 1962) ..nu........0.0.....-csasesccsoserscseeesesees 8
47 Fed. Reg. 7836 (Feb. 23, 1982) .............eccssssssecsssvssecesarsesscesssees 8
63 Fed. Reg. 39,857 (July 24, 1998) ............ceccccsssesssesnessnnsneens 12
67 Fed. Reg. 80,186 (Dec. 31, 2002).............cccsssseseesssensseeseaserens 12
68 Fed. Reg. 61,248 (Oct. 27, 2003) ...........ccccscsesseeeseeees 18, 27, 28
70 Fed. Reg. 61,081 (Oct. 20, 2005) .........--..ccccceceseeeseeees 24, 27, 28
Other Authorities
EE 16
RG Contam, Ge, TD CI cercrcccecersrnsrncsseenenqernernemennntamentante 17
Joint Hearing on NSR Issues Before the Senate
Environment and Public Works Comm. and the
Senate Judiciary Comm., 107th Cong. (July 16, 2002)..12, 13
Alabama Power Co. Petition for Adjustment of Rate
CNP, Order at 1, Docket Nos. 18117, 18416 (Nov.
Bae rte canansceninnsecnnansssintpetseneinesaieampanciatenpitininientpngeintenbnintie 25
Alabama Power Co. Petition for Revised Rate ECR
Factor, Order at 1, Docket No. 18148 (Dec. 15,
vii
Maryland Department of the Environment,
Maryland Clean Power Rule: Frequently Asked
Questions, www.mde.state. md.us/ Air/md_cpr.
Sec. William G. Ross, Jr., N.C. Dep’t of Env’t and Nat
Resources, North Carolina’s Clean Smokestacks
Act, www.ncair.org/news/leg/cleanstacks.shtm ........
INTEREST OF AMICI
In the Clean Air Act, Congress assigned to the States the
primary responsibility for the day-to-day regulation of air
pollution. “In the proper discharge of their responsibilities
to implement the [Act] in different conditions and localities
nationwide, the States maintain permanent staffs within
specialized agencies.” Alaska Dep’t of Envtl. Conservation v.
EPA, 540 US. 461, 516 (2004) (Kennedy, J., dissenting).
These state environmental regulators are committed public
servants who “take pride in their own resourcefulness,
expertise, and commitment to the law ....” Id.
The amici States oppose EPA’s sweeping, enforcement-
inspired interpretation of the Clean Air Act’s NSR/PSD
provisions for three reasons, all of which relate to the States’
role as the principal front-line enforcers of the Act's re-
quirements. Specifically, EPA’s current reading -
e Contradicts EPA’s earlier interpretations and, in-
deed, EPA’s past guidance to state regulators;
e Envisions a breathtaking transfer of enforcement
authority from the States to the federal govern-
ment and thus undermines the Clean Air Act's
federalism-respecting foundations; and
e Risks needlessly overwhelming the limited re-
sources available to state environmental agencies.
This Court should reject EPA’s current interpretation-
qua-litigating-position. Doing so will encourage principled
agency decisionmaking, preserve the state-federal balance,
and ensure a robust, yet manageable, NSR/PSD program.
SUMMARY OF THE ARGUMENT
EPA’s current litigating position concerning the Clean
Air Act's NSR/PSD rules (1) flatly contradicts its own earlier
interpretations and guidance to States, (2) violates the
fundamental principles of federalism that underlie the Act,
(3) risks needlessly overwhelming the state regulators who
2
are responsible for the Act's day-to-day implementation,
and (4) entails hidden pitfalls even as a matter of environ-
mental policy. The Court should reject it.
1. EPA’s litigating position (which, with respect, is all it
is) is not entitled to deference, for two reasons. First, EPA
has consistently blessed state environmental regulators’
NSR/PSD interpretations contrary to the one it now urges.
The Alabama Department of Environmental Management's
experience is illustrative: Consistent with express EPA
guidance, ADEM initially interpreted - and has since then
consistently interpreted - its own NSR/PSD rule to require
an increase in a unit's hourly emission rate as a prerequisite
to “major modification” analysis. Despite its constant
supervision of ADEM’s program (right down to its review of
individual NSR/PSD permits), EPA has never once sug-
gested that ADEM misunderstands the rules’ text or pur-
pose. Second, and more generally, EPA’s own approach to
the rules here at issue has been frightfully inconsistent.
Indeed, during the last 25 years, EPA has at seven different
junctures offered at least three different and mutually
exclusive interpretations of those rules.
2. On two grounds, EPA’s enforcement-inspired inter-
pretation undermines the Clean Air Act’s carefully cali-
brated state-federal enforcement scheme, which charges the
States with primary enforcement responsibility. First,
because under it, nearly every change made to every compo-
nent of every sub-par unit would trigger application of
stringent new NSR/PSD emission-limit requirements, EPA's
sweeping reading would cause the exception of federal
intervention to swallow the rule of state control. Second,
there is a straightforward - and federalism-respecting -
solution for States that want tougher new-source controls:
they should simply enact them as a matter of state law. The
Clean Air Act establishes a baseline of protection sufficient
to safeguard human health and safety, but by its own terms
it also expressly invites States to tighten requirements as
they see fit and thus act as Brandeisian “laboratories.”
3
3. EPA's litigating position - which, again, would make
nearly every tweak to an existing plant the occasion for
rigorous pre-construction review - is also wildly impractical.
Our chief concern here is the overwhelming burden with
which EPA’s current interpretation would saddle the state
regulators tasked with the ground-level enforcement of
Clean Air Act requirements. If on top of their existing duties
- developing and implementing SIPs and processing NSR
and PSD applications under current law - state regulators
had to deal with the flood of new requests that EPA’s
current view would unleash, the burden would overwhelm
existing resources, leading either to an administrative
breakdown, a bureaucratic explosion, or both.
4. Important public-policy considerations counsel
against EPA’s litigating position, as well. First, of course,
there is the sheer expense (i.e., the permitting process itself
plus the required retrofits) that EPA’s current view would
entail. Our concern here is less with industry costs as such
than with the near-certainty that industry would simply
pass its own increased costs on to consumers in the form of
rate hikes. That concern is particularly acute where, as here,
the affected consumers are utility rate-payers, whose inter-
ests state Attorneys General are statutorily obliged to
protect. Second, there are good clean-air reasons to oppose
EPA’s enforcement position. The cost - in money, time, and
labor - of EPA’s enforcement initiative will create what EPA
itself has called a “perverse” incentive for industry to
eschew upgrades in favor of limping by on old, deteriorat-
ing, and environmentally-unfriendly equipment.
5. Petitioners’ jurisdictional argument clearly misses
the mark. Section 307(b) encompasses only challenges to
“promulgatiions}” of “nationally applicable regulations”
and other EPA “final action[s].” This case, which concerns
the propriety of EPA’s application of its NSR/PSD rules in
the context of an ongoing enforcement action, involves no
such challenge. Moreover, it simply cannot be the law that
when EPA itself initiates an enforcement proceeding in
district court, the target is faced with the choice of either (1)
4
declining to defend and accepting an adverse judgment or
(2) instituting a duplicative proceeding in the D.C. Circuit.
ARGUMENT
This brief is no apology for industry. In a perfect world,
with blank statute books and unlimited resources, the amici
States might opt for the type of enforcement agenda EPA is
pursuing here. Our disagreement with EPA (with one
notable exception) is less about environmental policy than
about the legality and real-world practicality of EPA’s
current enforcement initiative. As matters now stand, EPA’s
actions are both illegal and wildly impractical.
I. EPA’s Current Litigating Position Is Not Entitled to
Deference, Particularly Given EPA’s Consistent En7
dorsement of State Agencies’ Longstanding PSD Inter7
pretations to the Contrary.
We start with the question of legality. The notion that
there is only one plausible reading of the Clean Air Act's
1980 PSD rule,’ requiring intensive pre-construction review
based solely upon a projected increase in a plant's hours of
operation (Pet. Br. 2, 25, 34, 49; EPA Br. 13, 19-20; NY Br. 7),
is, as we will explain, plainly wrong. So, too, is the related
suggestion that EPA has had anything like a “longstanding”
interpretation (Pet. Br. i; NY Br. 1; NJ Br. 2) to that effect
1 45 Fed. Reg. 52,676 (Aug. 7, 1980) (codified at 40 C.F.R. §51.166 (1987).
2 To its credit, EPA itself does not even claim here to have had a longstand-
ing position concerning the meaning of the 1980 PSD rule. And with good
reason; as we will show, EPA’s own reading of the rule has been anything
but consistent. See infra at 10-14. Indeed, even its brief in this Court seems
more than a bit schizophrenic. At one point, for instance, EPA asserts that
“[t}he only reasonable construction of the PSD regulations is that a physical
change that increases a source’s hours of operation is a ‘modification.””
EPA Br. 20 (emphasis added). A bit later, EPA says, quite differently, that
“it would have been permissible for EPA to” construe the term “ modifica-
tion” for PSD purposes the way it is used in the NSPS program, i.c., to
require an increase in the hourly rate of emissions. /d. at 35.
5
Duke itself has made the textual case against EPA’s cur-
rent reading of the 1980 PSD rule (Duke Br. 33-36), and there
is no point in replowing that ground here. Our purpose is to
demonstrate that EPA’s current hours-of-operation-based
litigating position does not warrant deference (1) because
the agency has consistently blessed state environmental
regulators’ interpretations to the contrary; and (2) more
generally, because it is just the latest in a bob-and-weave
succession of contradictory agency pronouncements.
A. EPA Has Consistently Blessed State7Agency PSD
Interpretations Contrary to the One It Now Ad7
vances.
As Justice Kennedy recently observed, “[iJn the proper
discharge of their responsibilities to implement the [Clean
Air Act] in different conditions and localities nationwide, the
States maintain permanent staffs within specialized agen-
cies.” Alaska Dep’t of Envtl. Conservation v. EPA, 540 US. 461,
516 (2004) (Kennedy, J., joined by Rehnquist, C.J., and Scalia
and Thomas, JJ., dissenting). “These state employees, who
no doubt take pride in their own resourcefulness, expertise,
and commitment to the law, are the officials directed by
Congress to make case-by-case, site-specific, determinations
under the Act.” Id. In the State of Alabama - whose experi-
ence is described below merely for purposes of illustration -
the agency to which Justice Kennedy’s observation refers is
the Alabama Department of Environmental Management
(“ADEM”).
From the very beginning, ADEM has understood that
PSD “major modification” review is triggered only by
activity that causes an increase in a plant's hourly rate of
emissions and not, importantly, by a recovery or extension
of the plant’s hours of operation. ADEM first promulgated
PSD regulations in January 1981. Later that same year, those
regulations were expressly “approv[ed]” by EPA as “com-
ply[ing] with the latest guidance issued by EPA to assist
States in preparing State implementation plan (SIP) revisions
for PSD.” 46 Fed. Reg. 55,517 (Dec. 10, 1981) (codified at 40
6
C.F.R. §52.50). As both ADEM’s current Air Division chief
(since 1996) and his predecessor (chief from 1982 to 1996)
have testified, ADEM’s EPA-approved PSD regulation has
always “focused on the maximum hourly rate of emissions,”
such that “[o]nly if the maximum hourly rate of emissions
increased as the result of a project or activity could the
activity potentially trigger PSD requirements.” Decl. of
Richard E. Grusnick, Former Chief, ADEM Air Division
(“Grusnick Decl.”), $9, in United States v. Alabama Power Co.,
372 F. Supp. 2d 1283 (N.D. Ala. 2005) (App. A to this brief).
In other words, ADEM has at all times read its PSD regula-
tion to mean that “major modification” review is triggered
only by “those projects or activities that increase the maxi-
mum capacity of a unit or facility to emit more pollution on
an hourly basis,” and, equally importantly, not by “a project
or activity that is followed by an increase in the availability
or utilization of a facility.” Decl. of Ronald W. Gore, Chief,
AEDM Air Division (“Gore Decl.”), {5, 7, in Alabama Power,
372 F. Supp. 2d 1283 (App. B to this brief).
Notably, ADEM’s understanding and application of the
term “major modification” - 1e¢., to focus exclusively on
activity that results in an hourly-rate increase - “has not
changed substantively since [the PSD rule’s] original adop-
tion in 1981.” Grusnick Decl. 910. Indeed, ADEM’s inter-
pretation of the PSD regulation has been a model of consis-
tency. Only three individuals have headed ADEM’s Air
Division since the PSD program came onto the scene in 1980.
Under their principled leadership - and through the tenures
of seven different Governors (four Democrats and three
Republicans) and six different Attorneys General (three of
each party) - ADEM has persisted in its hourly-rate-based
understanding of the “major modification” analysis.
ADEM has interpreted its EPA-approved PSD regulation
to focus on hourly-rate increases and to exclude hours-of-
operation increases not only because that is the most sensi-
ble reading of the regulation’s language but also, and more
significantly for present purposes, because that is how EPA
itself said to interpret it. In January 1981, and then again in
7
June of that same year - just about the time ADEM was
requesting and obtaining EPA’s blessing for its own PSD
regulations - EPA’s Director of Stationary Source Enforce-
ment, Edward Reich, confirmed in two separate memoranda
that PSD applicability “is determined by evaluating any
change in [hourly] emissions rates caused by” a physical or
operational change. JA 28. The reason, Reich explained,
was that, otherwise, “[a]ctual emissions could increase only
if there is an increase in the production rate or hours or
operation, both of which are specifically exempt from PSD
review.” Id. (citing 40 C.F.R. §52.21(b)(2)(iii)(f)); accord JA 35
(“H]n the absence of any SIP or permit limitations,” the
“increase in hours of operation at the power plant” would
not “be considered a modification”) (citing 40 CF.R.
§52.21(b)(2)(iii)(e) and (f)).°
To precisely the same effect, just a year later, EPA’s re-
gional chief of the Air & Waste Management Division, James
Wilburn, issued a report “to all state and local agency
directors” - i.e., to agencies like ADEM - one purpose of
which was to alert state regulators to “interpretations of EPA
regulations.” U.S. EPA, Region IV, Memorandum No. 4AW-
AM, at 1 (July 12, 1982) (App. C to this brief). The report
addressed the very question presented here, and answered it
decisively in favor of ADEM’s understanding:
Question: A source to be modified will be subject to
PSD due to a significant increase in SO2 emissions.
After the modification there will be no increase in the
hourly particulate emissions. The source presently
operates at 4,000 hours per year. If the PSD permit
would allow 7,000 hours per year, would this be
judged a significant increase in particulate emissions,
3 The concerted efforts to marginalize Mr. Reich as just some guy - or,
worse, a rogue bureaucrat - are disingenuous. See EPA Br. 13 (“mid-level
EPA official”); NY Br. 18 (“single agency employee”). Mr. Reich was not
just some guy, he was the guy - the director of the very EPA division
whose responsibility it was to speak to the correct interpretation of the
PSD regulations.
8
and cause the source to be subject to PSD for particu-
late?
Answer. No. Since the modification does not cause
any increase in [the referenced hourly particulate]
emissions, no increase in annual emissions should be
calculated.
Id. at 2. Notably, North and South Carolina, like Alabama,
are in EPA “Region IV”; accordingly, the state regulators
whose permitting decisions are being second-guessed in this
enforcement action presumably received Mr. Wilburn’s
directive, as well. What is more, North and South Carolina,
like Alabama, adopted their own PSD rules (and obtained
EPA approval) during the Reich-Wilburn era. See 47 Fed.
Reg. 7836 (Feb. 23, 1982) (North Carolina); 47 Fed. Reg. 6017
(Feb. 10, 1982) (South Carolina).
It should be enough that agencies like ADEM acted
against the backdrop of EPA’s own programmatic advice in
crafting and implementing state PSD regulations. But there
is much more. Having initially approved ADEM’s PSD
rules as in “compl{iance] with the latest guidance issued by
EPA” concerning the PSD program and codified those rules
into federal law (supra at 5), EPA has during the last 25 years
repeatedly blessed ADEM’s hourly-rate-based understand-
ing of its PSD regulation. Initially, and most generically, as
an exercise of its “oversight responsibility to ensure that the
state program satisfied the requirements of the Clean Air
Act,” EPA “would periodically issue policy memoranda
which would provide EPA’s guidance on major air program
policy issues.” Grusnick Decl. 916. None of those docu-
ments, however, ever “communicate[d] to ADEM the
interpretations of PSD preconstruction permitting require-
ments that [EPA] advances” in the present enforcement
initiative. Id. |
More specifically, “EPA had numerous, regular oppor-
tunities to identify ADEM’s policies and offer suggestions in
the event it disagreed with ADEM on a point of interpreta-
tion.” Id. $17. .First, EPA conducted “annual on-site audit[s]
of ADEM’s Air Program”; these audits “generally included a
9
mid-year review where Regional EPA staff members would
visit ADEM, meet with staff, perform file reviews of indi-
vidual plants, and review other records.” Id. Second, as part
of the “federal grant process” there was an “annual negotia-
tion of commitments between EPA and the state” during
- which EPA could identify topics of “high priority” and
leverage “commitments from ADEM.” Id. Third, and
separately, EPA and ADEM negotiated annual Clean Air Act
enforcement agreements covering all aspects of compliance
and enforcement, including, the PSD program. Significantly
here, these agreements stressed the importance of EPA and
ADEM “resolving disputes, especially differences in interpreta-
tion of regulations or program goals as they may affect resolution
of individual instance[s] of non-compliance.”4 The agreements
also provided that EPA and ADEM would “conduct
monthly conference calls” as a means of ensuring a coordi-
nated enforcement strategy.> Tellingly, “[n]o audit or grant
discussion ever targeted implementation of the modification
provisions of the PSD regulations consistent with EPA’s
current interpretation.” Grusnick Decl. 418.
Finally, and more specifically still, as part of what this
Court has called its “sweeping” “surveillance,” “oversight,”
“supervisory,” and “checking” responsibilities, see Alaska,
540 U.S. at 469, 484, 485, 486, 487, 488, 490, 492, 496, 502, EPA
routinely reviewed individual PSD permits issued by
ADEM. To facilitate that review, the Clean Air Act itself
required ADEM to inform EPA specifically of “every action’
taken in the course of the permit approval process” and
further guaranteed EPA the right to submit comments
concerning proposed permits. Id. at 508 (Kennedy, J.,
dissenting) (quoting 42 U.S.C. §7475(d)). Moreover, as
illustrated by the Alaska decision itself - the central premise
of which is that EPA can and should look over state agen-
* Alabama/EPA Compliance Assurance Agreement 2 (1996) (emphasis
added) (Appendix D to this brief).
5 Id. ADEM'’s files contain similar agreements for 1986, 1989, and 1990.
10
cies’ shoulders to ensure the proper administration of the
PSD program - EPA could always have vetoed ADEM’s
issuance of a permit or otherwise moved to block a change
authorized by ADEM. See id. at 473-74, 480-81 (majority
opinion). Tellingly, it never did.
The point here is simply this: Knowing full well
ADEM’s_ hourly-rate-based understanding of the PSD
modification rule (and, indeed, having counseled ADEM to
embrace that understanding to begin with), it was incum-
bent upon EPA to speak up if it thought ADEM’s under-
standing or application of that rule was out of whack.
Despite hundreds of opportunities, EPA never did so. Of
course, if EPA believed ADEM was way off track (and there
is, to be sure, a huge practical difference between ADEM’s
consistent interpretation and the one that EPA urges in this
litigation), it could have issued a “SIP call” requiring ADEM
either to change its ways or to forfeit its permitting authority
altogether. See 42 US.C. §7410(c)(1), (k)(5).. But ADEM
never received so much as a tap on the shoulder. By now
pulling the rug out from underneath ADEM 20 years after
the fact, EPA has “indulge[d]” in precisely the “inequitable
conduct” this Court implicitly forbade in Alaska, 540 US. at
495. See also id. (emphasizing that it is essential for EPA “to
act on a timely basis” if it is going to second-guess state
regulators); id. at 513 (Kennedy, J., dissenting) (recognizing
the “need for finality in state permitting decisions” and that
“a post hoc veto procedure” upsets “reliance and expecta-
tion interests”). ,
B. EPA’s Own Pronouncements Concerning the PSD
Rule Have Been Frightfully Inconsistent.
Alabama’s interpretation of the PSD rule’s modification
provisions ~ i.e., to hold hours of operation constant and to
require as a prerequisite to “major modification” analysis an
increase in the hourly emission rate - is thus not only EPA-
blessed but also truly longstanding and consistent EPA
itself cannot make a similar claim. It has, with respect, been
all over the map. Presently, of course - by which we mean
11
currently in the life of this particular enforcement proceed-
ing ~- EPA advances a so-called “actual-to-projected-actual”
understanding of the 1980 PSD rule. Pursuant to that
interpretation, an increase in annual emissions may be
triggered by an increase in a source’s hours of operation
standing alone, that is, even absent an increase in the
source’s hourly emission rate or, indeed, despite a decrease
in that rate. United States v. Duke Energy Corp., 278 F. Supp.
2d 619, 640 (M.D.N.C. 2003) (describing EPA’s position).
That has not always been EPA’s view. In fact, since its
adoption in 1980, EPA has advanced at least three different and
mutually exclusive interpretations of the PSD rule. Tracing the
evolution can be a dizzying exercise:
Take One: Initially, in 1981, EPA endorsed the so-
called “actual-to-actual” test (used, e.g., by ADEM),
pursuant to which a “major modification” occurs
only where activity increases a unit's hourly emis-
sion rate. See supra at 5-8.
Take Two: Then, in its 1988 “WEPCo determination,”
EPA asserted that the “actual-to-potential” test, pur-
suant to which post-change emissions are theorized
by multiplying a unit's maximum emission rate by
the total number of hours in an entire year, was the
only permissible way to measure PSD modifications.
In so asserting, EPA stated categorically that the 1980
PSD regulations “provide no support for” the actual-
to-projected-actual test that it now urges. JA 256 n.7.
Take Three: In the wake of the Seventh Circuit's re-
jection of its actual-to-potential test, Wisconsin Elec.
Power Co. v. Reilly, 893 F.2d 901, 917 (7th Cir. 1990) -
and, seemingly, that court's instruction to apply an
actual-to-actual test using “present hours and condi-
tions,” id. at 918 n.14 - EPA went back to the drawing
bourd. It did not, however, return to its actual-to-
actual interpretation but, instead, embraced the very
actual-to-projected-actual test it had earlier insisted
had “no support” in the regulation. JA 66-72.
12
Take Four: In its 1992 “WEPCo Rule,” EPA formally
adopted the once-rejected actual-to-projected-actual
test for measuring emissions but, curiously, made it
optional and available only to utilities. See 40 C.F.R.
§51.166(b)(21) & (b)(32) (1993).
Take Five: Then, in 1998, EPA asserted in a proposed
rule that the actual-to-potential test (abandoned after
WEPCo) was and had always been the sole means of
measuring emissions increases for PSD purposes ~ at
least for non-utility sources. See 63 Fed. Reg. 39,857,
39,859 n.4 (July 24, 1998).
' Take Six: In 2002, EPA promulgated a new, manda-
tory actual-to-projected-actual methodology for all
existing sources (not just utilities) and, in so doing,
reiterated its view that the actual-to-potential test
remained the governing standard under the preexist-
ing 1980 PSD rule. See 67 Fed. Reg. 80,186, 80,191-92,
80,199 (Dec. 31, 2002).
Take Seven: Finally, in litigating this very case, EPA
initially invoked the actual-to-potential test as. the
appropriate means of measuring increases under the
1980 rule, but appears to have settled, at last, on a
version of the actual-to-projected actual analysis. See
Duke Energy, 278 F. Supp. 2d at 640 & n.17.
In the words of its own former general counsel, EPA’s
current “multi-billion dollar’ NSR/PSD enforcement
initiative rests “on the premise that the same words in the
law meant one thing in 1985, another thing in 1992, still
another in 1996, yet another in 1998, and will someday mean
something still different in the future.” Joint Hearing on NSR
Issues Before the Senate Environment and Public Works Comm.
and the Senate Judiciary Comm., 107th Cong., pp. 2-3 (July 16,
2002) (statement of E. Donald Elliott) (“Elliott NSR Test.”). It
is a dubious premise.
As a practical matter, New Jersey is exactly right when it
says that “[tJhe States’ ability to plan for and meet their
obligations under the CAA depends on the stability of
13
nationwide regulations.” NJ Br. 8. The problem is that
EPA’s approach to the NSR/PSD rules has been anything
but “stabfle].” Quite the contrary, EPA’s “many changing
interpretations of NSR over the years have created a legal
mess of baffling complexity ....” Elliott NSR Test. at 1.
More importantly, as a legal matter, EPA's “zigs and zags
represented by its contradictory post-WEPCO statements
and rules” and its failure to speak “with one voice, or a
consistent voice, or even a clear voice, on this issue,” Ala-
bama Power, 372 F. Supp. 2d at 1306, fatally undermine its
claim to deference. See, e.g., Good Samaritan Hosp. v. Shalala,
508 U.S. 402, 417 (1993); INS v. Cardoza-Fonseca, 480 U.S. 421,
446 n.30 (1987). That is particularly true where, as here, the
agency's interpretation has “fluctuated” even “as [the] case
has progressed.” North Haven Bd. of Educ. v. Bell, 456 U.S.
512, 539 n.29 (1982).
It is true, of course, that “[a]n initial agency construction
is not instantly carved in stone.” Chevron, U.S.A., Inc. v.
NRDC, 467 US. 837, 863 (1984). But it is equally true that
““To]nce an agency gives its regulation an interpretation
which, the case law reflects, it may do either through re-
gional guidance determinations (e.g., the Wilburn ere or,
a fortiori, through formal, central-office guidance (e.g.,
Reich memos) - “‘it can only change that interpretation as “~
would formally modify the regulation itself: through the
process of notice and comment rulemaking.” Alaska Prof'l
Hunters Ass'n v. FAA, 177 F.3d 1030, 1033-34 (D.C. Cir. 1999)
(quoting Paralyzed Veterans of America v. D.C. Arena, 117 F.3d
579, 586 (D.C. Cir. 1997)) (finding that FAA had unlawfully
changed an interpretation earlier adopted by its Alaskan
Region); accord, e.g., Caruso v. Blockbuster-Sony Music Enter-
tainment Centre at the Waterfront, 193 F.3d 730, 737 (3d Cir.
1999) (Alito, J.). Given that its current, enforcement-inspired
interpretation of the 1980 PSD rule contradicts its earlier
view (or views, as the case may be), EPA’s position here can
be understood only as a “convenient litigating position,” to
which no deference is due. Bowen v. Georgetown Univ. Hosp.,
488 U.S. 204, 212-13 (1988).
14
Se. @&
It is worth pausing briefly to take stock of the story that
EPA’s present enforcement initiative - and the newfound
view of the NSR/PSD rules that underlies it - requires the
Court to believe. The current batch of enforcement actions
alleges rampant, if not near-universal, non-compliance with
NSR/PSD rules stretching back some 20 years. How, on
EPA’s retelling, did we get to this point? First, we must
assume that nearly every major utility-industry player (and,
more particularly, every major player’s lawyers) either
fundamentally misunderstood or blatantly ignored EPA
guidance on the meaning of the term “major modification.”
Second, and worse, we must assume that the state environ-
mental agencies that reviewed and approved the hundreds
of building projects now under challenge (ADEM in Ala-
bama Power's case, the North Carolina Department of
Environment and Natural Resources in Duke's) likewise
either misunderstood or ignored EPA guidance. Finally, and
most bizarrely, we must assume that the EPA regulators
themselves, whose very business it was to look over the
States’ shoulders, were (at best) asleep at the wheel. EPA’s
story here is either an elaborate conspiracy theory or a
monument to bureaucratic incompetence. Occam’s Razor
suggests a different explanation: EPA’s current litigating
position just wasn’t the prevailing understanding of
NSR/PSD applicability during the two decades that pre-
ceded the current enforcement initiative’s launch in 1999.
II. EPA’s Litigating Position Undermines the Clean Air
Act’s Carefully Calibrated State7Federal Enforcement
Scheme.
Congress enacted the Clean Air Act with federalism
firmly in mind. There are two important federalism-related
points worth making here, neither of which the state amici
supporting petitioners seem to have come to grips with
First, whereas the Act makes States primarily responsible for
regulating air pollution, and carves out NSR/PSD as a
narrow exception to that general rule of state control, the
15
position advocated by petitioners and their state amici
would reverse matters entirely. It would make almost every
tweak to an existing source the occasion for intrusive federal
review and intervention. Second, by its very terms, the
Clean Air Act establishes only a regulatory baseline; States
with the desire and the gumption can always enact tougher
environmental controls. States that have declined to do so
have no standing to complain.
A. Under EPA’s Litigating Position, the Exception of
Federal Intervention Would Swallow the Rule of
State Control.
It is a well-recognized fact, as the state amici supporting
petitioners seem to appreciate, that the Clean Air Act “relies
on a close and equal partnership between federal and state
authorities to accomplish congressional objectives.” Alaska,
540 U.S. at 518 (Kennedy, J., dissenting). In the cooperative
scheme established under the Act, States do not play “the
role of mere provinces or political corporations” but, “in-
stead, of coequal sovereigns entitled to the same dignity and
respect.” Id. Indeed, the Act's language itself makes clear
that “air pollution prevention ... and air pollution control at
its source is the primary responsibility of States and local
governments.” 42 U.S.C. §7401(a)(3) (emphasis added); see
also id. §7407(a) (States have “primary responsibility”).
Pursuant to the scheme that Congress established, EPA
initially sets national ambient air quality standards
(“NAAQS") to protect public health and welfare, 42 U.S.C.
§7409, and States, in turn, develop detailed state implemen-
tation plans (“SIPs”) that specify schedules, compliance
_ timetables, and emission limitations for specific sources,
including electric utility plants, id. §7410(a). States must
include in their SIPs a program for pre-construction review
of construction activity that creates new pollution, the aim
being to ensure that pollution not originally accounted for
under a SIP is reviewed and regulated to protect the
NAAQS before it is emitted. Jd. §7410(a)(2)(D). EPA must
approve a SIP if it meets the criteria specified in §7410(a).
16
See Train v. NRDC, 421 U.S. 60, 78-79 (1975).
As a result of the state-federal balance that Congress
struck, EPA is generally forbidden to micromanage state
emission-control policies with respect to existing sources.
Rather, while EPA is “plainly charged by the Act with the
responsibility for setting” the NAAQS, “[j]ust as plainly ... it
is relegated by the Act to a secondary role in the process of
determining and enforcing the specific, source-by-source
emission limitations which are necessary if the national
standards it has set are to be met.” Id. at 79. Congress gave
EPA “no authority to question the wisdom of a State’s
choices of emission limitations if they are part of a plan
which satisfies the standards” of §7410(a). Id. Rather, so
long as the “ultimate effect of a State’s choice of emission
limitations is compliance with the national standards for
ambient air,” a State is “at liberty to adopt whatever mix of
emission limitations it deems best suited to. its particular
situation.” Id.; see also Union Elec. Co. v. EPA, 427 U.S. 246,
269 (1976) (“Congress plainly left with the States, so long as
the national standards were met, the power to determine
which [existing] sources would be burdened by regulation
and to what extent.”).
The NSR/PSD rules at issue here constitute a narrow
exception to the general rule under the Act that States have
primary responsibility to determine whether and how to
regulate pollution sources. Indeed, in Train, this Court
specifically referred to the emission limits imposed by the
Act’s New Source Performance Standards (“NSPS”) provi-
sions, see 42 U.S.C. §7411, as an “[e]xception{]” to EPA’s
decidedly “secondary role” in “the process of determining
and enforcing the specific, source-by-source emission
limitations.” 421 U.S. at 78 & n.16. When enacting the NSPS
program, Congress considered a more sweeping program
that would have subjected existing sources, as well as new,
to federally-established limits. Significantly, though, noting
cost considerations and the difficulty of retrofitting existing
sources, Congress opted not to pursue that course, see S.
Rep. No. 91-1196, at 15-16 (1970); instead, while requiring
17
new sources to install the latest control technologies, Con-
gress left existing sources subject to state-established SIP
limits. See 116 Cong. Rec. 42,520 (1970). The Train Court's
emphasis on NSPS exceptionalism, of course, carries over
jot-for-jot to the NSR/PSD program at issue here, for the
simple reason that the NSR program defines the term
“modification” - which for present purposes is what triggers
new NSR-driven emission limits and thus displaces tradi-
tional state control - by reference to the NSPS program’s use
of the same term. See 42 U.S.C. §§7479(2)(C), 7501(4). See
also Alaska, 540 U.S. at 491 (even the PSD program “places
primary responsibilities and authority with the States,
backed by the Federal Government”).
EPA’s position here turns the Clean Air Act on its head
and causes the exception of federal intervention to swallow
the rule of state control. Under EPA’s current regulatory
interpretation, the rigorous NSR/PSD permitting process
(and the establishment of new emission limits) would be
triggered by any physical or operational change to an
existing source that facilitated any increase in hours of
operation and thereby increased annual emissions - even
without a corresponding hourly-rate increase or, for that
matter, despite an hourly-rate decrease. But of course nearly
every repair or replacement of damaged, deteriorating, or
malfunctioning equipment will result in an hours-of-
operation increase (that being the point of the repair) and
thereby - assuming constant, or even marginally reduced,
rates of emission - result in an increase in actual emissions.
Accordingly, under EPA’s view, nearly every physical
change made to every component of every sub-par unit
would trigger application of new NSR/PSD requirements.
(Indeed, when wearing its rulemaking hat, EPA has recently
and candidly conceded that its position “in briefs in various
enforcement-related cases” - presumably a reference to
18
cases like this one - would make “virtually all changes, even
trivial ones,” subject to NSR requirements.®)
The risk is not hypothetical. Take, as just one example, a
1996 enforcement proceeding brought by EPA against the
Georgia-Pacific Corporation. There, EPA alleged that
Georgia-Pacific had, at a number of its plants (two of which
were in Alabama), engaged in “construction” or “major
modification” activity without the required PSD permits.
See Consent Decree at 1, United States v. Georgia-Pacific Corp.,
No. 1 96-CV-1818-FMH (N.D. Ga. July 18, 1996). That
enforcement proceeding was resolved pursuant to a consent
decree, which constituted “full settlement” for, among other
things, the PSD “modifications” listed in an appendix to the
decree. Id. at 35-36. The catalogue of charged “modifica-
tions” spans 54 pages, numbers 994 individual items, and
stretches back some 19 years. Id. Schedule C. Many of the
items on the list - e.g., “Resin/ glue reformulation,” “ Auxil-
iary feed screw installed,” “Single head sander,” “patch-
line,” “Ramp for loading mulch” - hardly seem like the sorts
of changes Congress had in mind when used the term
“modification” as the statutory trigger for rigorous federal
PSD review. Id. Schedule C at 1, 3, 9, 11, 14.7
The point here is not, as a policy matter, that more or less
stringent controls are preferable. Rather, the point is that in
the light of the Clean Air Act's federalism-respecting under-
pinnings, this Court should be slow to assume that Congress
could possibly have intended to permit such a wholesale
6 68 Fed. Reg. 61,272 (Oct. 27, 2003), vacated, New York v. EPA, 443 F.3d 880
(D.C. Cir. 2006).
7? Importantly, under petitioners’ and EPA’s view of the law (as articulated
in the lower courts), these changes likely would not be exempt from PSD
review under 40 C_F.R. §51.166(b)(2)(a)(iii)'s “routine maintenance, repair
and replacement” exclusion. And therein lies the practical problem with
petitioners’ and EPA’s arguments: They would make PSD applicable “to
virtually any capitalized maintenance or repair project that prevented
enough downtime to breach the emissions increase thresholds.” Alabama
Power, 372 F. Supp. 2d at 1297.
19
transfer of regulatory responsibility from the States to the
federal government.
B. There Is a True Federalism7Respecting Solution
Here: If a State Wants Stricter New7Source Con7
trols, It Should Simply Enact Them.
The amici States backing petitioners and the EPA here
invoke the value of federalism to support their positions.
See, e.g., NJ Br. 1, 5, 10; NY Br. 1. It is not, with respect, a
notion of “federalism” with which we are familiar. It is, as
we will show, federalism-in-reverse.
The genius of federalism, properly understood, is per-
haps best captured by Justice Brandeis’ famous “laboratory”
metaphor: “It is one of the happy incidents of the federal
system that a single courageous State may, if its citizens
choose, serve as a laboratory; and try novel social and
economic experiments without risk to the rest of the coun-
try.” New State Ice Co. v. Liebmann, 285 U.S. 262, 311 (1932)
(Brandeis, J., dissenting); accord, e.g., United States v. Lopez,
514 US. 549, 581 (1995) (Kennedy, J., concurring). In other
words, federalism leaves States free to make tough social-
policy decisions for themselves. As we will explain, the Clean
Air Act accommodates - indeed, encourages - Brandeisian,
laboratory-style federalism. But New York, New Jersey, et
al., seem to have a far more ambitious program in mind.
Rather than making decisions for themselves, they want to
upload their own notions of good environmental policy into
federal law and thereby export them to everyone else. What-
ever kind of solution that may be, it is not one that can be
squared with - indeed, it is one that subverts - traditional
federalism principles.
Petitioners’ state amici’s mistake, moreover, is not just
one of terminology. New York's brief opens with a warning
about the “dire ramifications” of emissions from “uncon-
trolled plants,” which, it says, “kill tens of thousands of
Americans annually and sicken hundreds of thousands of
others.” NY Br. 3. But that argument, with respect, is a
straw man, as is any suggestion that affirmance here would
20
allow plants to “proceed without any scrutiny by the States.”
NY Br. 2. By its own express terms, the Clean Air Act sets
only a baseline of protection. That is, it imposes minimum
compliance requirements and explicitly invites States to
tighten them as they see fit As relevant here, §116 of the
Clean Air Act unambiguously provides that -
nothing in this chapter shall preclude or deny the
right of any State or political subdivision thereof to
adopt or enforce (1) any standard or limitation re-
specting emissions of air pollutants or (2) any re-
quirement respecting control or abatement of air pol-
lution; except that if an emission standard or limita-
tion is in effect under an applicable implementation
plan or under section 7411 or section 7412 of this title,
such State or political subdivision may not adopt or
enforce any emission standard or limitation which is
less stringent than the standard or limitation under
such plan or section.
42 US.C. §7416. The message is clear: States may of their
own accord adopt emissions limitations (here, PSD require-
ments) that are more rigorous than those established by
federal law (here, the Clean Air Act’s own PSD rules). See
Union Elec., 427 U.S. at 256-57 (Clean Air Act “subject([s] the
States to strict minimum compliance requirements”).
The point is simply that if any State at any time wants
lower emissions caps or tighter permitting requirements, it
need only convince its Legislature to enact them and its Governor
to sign them. A few “courageous” States, see New State Ice,
285 U.S. at 311, of course, have had done just that. In 2002,
North Carolina enacted its own “Clean Smokestacks Act,”
which requires coal-fired power plants to reduce emissions
of NOx and SO) far more aggressively than federal law - by
roughly three-quarters over a 10-year period. N.C. Gen.
Stat. §143-215.107D(b)-(d). In addition, the Act specifies that
the State’s largest utilities “must achieve these emissions
through actual reductions at their 14 power plants in the
state - not by buying or trading emissions credits from
utilities in other states, as allowed under federal regula-
21
tions.” Sec. William G. Ross, Jr., N.C. Dep’t of Env’t and
Nat. Resources, North Carolina’s Clean Smokestacks Act,
www.ncair.org/news/leg/cleanstacks.shtml. The North
Carolina law is thus tougher than federal law on two counts
and, indeed, is touted as going “beyond the requirements of
the EPA’s SIP call.” Id.
More recently, Maryland, too, enacted a “Healthy Air
Act.” Md. Code. Ann. §2-1001 et seq. Over the course of the
next decade, the Maryland law will reduce NOx emissions
by 85%, SO2 by 80%, and mercury by 90%. See id. §2-1002;
Maryland Department of the "nvironment, Maryland Clean
Power Rule: Frequently Asked Questions, www.mde.state.
md.us/ Air/md_cpr.asp. Like North Carolina’s, Maryland’s
law prohibits “power plants from acquiring out-of-state
emissions allowances (trading credits) in lieu of adding
pollution controls locally.” Id. Thus, like North Carolina’s,
Maryland's law is in two respects “stronger than current
federal plans.” Id. It means, so its proponents claim,
“cleaner air in Maryland.” 1d.
Federalism, therefore, is working just the way the Fram-
ers - both of the Constitution and of the Clean Air Act —
intended. If New York, for instance, wants to ensure that its
own “efforts to prevent air quality from deteriorating” are
not “undermine[d]” (NY Br. 1), it should simply redouble
them. There are, to be sure, administrative and political
costs to enacting tough environmental controls - they are,
for better or worse, part of the calculus. What petitioners’
state amici cannot do, consistent with the notion of federal-
ism embodied in Clean Air Act §116 (or with any other
meaningful notion of federalism, for that matter), is to seek
to externalize those costs by free-riding a dubious interpreta-
tion of a federal regulation to their preferred policy out-
come.’
® Finally, if New York (or any other State) believes that emissions from
sources in other States are contributing to a violation of its own air-quality
22
Ill. EPA’s Litigating Position Has No Basis in the Real7
World Practicalities of Clean7Air Enforcement.
EPA’s interpretation of the applicable PSD rule is, as we
have said, not only illegal but also wildly impractical. We
want to focus briefly on practicalities.
Again, according to EPA, the rigorous PSD permitting
process is activated by any change to an existing source that
recovers lost productivity and thereby (even without a
corresponding emissions-rate increase or, indeed, despite an
emissions-rate decrease) increases annual emissions. The
problem, as we have explained, is that on EPA’s view, nearly
every change, however minor, qualifies, for the simple
reason that nearly every repair of a damaged or deteriorat-
ing part will allow for an hours-of-operation increase and
thereby - assuming constant, or even marginally reduced,
rates of emission - result in an increase in annual emissions.
Not only would that interpretation result in a breathtaking
transfer of regulatory authority from the States to the federal
government, but it would also impose a crippling burden
both on industry and on the state regulators who would be
tasked with its ground-level implementation.
Industry, of course, can speak for itself here. It is enough
for our purposes to point out the obvious. Most plants have
many units, and most units have many parts. Parts will go
down - and thus require repair or replacement - at different
and often unpredictable times. If, as our discussion of the
Georgia-Pacific consent decree shows (see supra at 18), even
relatively minor repair-and-replacement activities trigger the
PSD review process, that process will go on ad infinitum.
Imagine, for instance, that a section of tubes on hypothetical
Boiler No. 1 goes down. PSD review is activated. Just as
that section is set to emerge from the PSD process, a section
on Boiler No. 2 (or perhaps even a different component part
on No. 1) goes down, activating a new round of PSD review.
standards, Clean Air Act §126 provides a specific statutory remedy. See 42
U.S.C. §7426.
23
Given the sheer number of moving parts in the typical plant
(see, e.g., the 994 “modifications” cited in Georgia-Pacific’s
case) and the amount of time it takes to conduct a proper
PSD review and to issue a permit, see, e.g., Alaska, 540 US. at
516-17 (Kennedy, J., dissenting) (“[F]or a complex project,
the time for approval can take from five to seven years.”), it
is easy to see that the reviews would in many instances
overlap interminably, leaving plant operators in an inescap-
able regulatory Charybdis. (The problem would be exacer-
bated, of course, by the fact that PSD entails a pre-
construction permit process; so the plant operator wouldn't
even be able to begin fixing broken part No. 1 before it got
the final green light from regulators, by which point there
would probably be a broken part No. 2.)
Of greater and more immediate concern to us is the
overwhelming burden with which EPA’s interpretation
would saddle state environmental regulators. Put simply,
state agencies like ADEM would inevitably find themselves
unable to keep up. The backdrop here, of course, is every-
thing that state regulators already do. First, there is the
development of the initial SIP, which must include (among
other things) an EPA-approved PSD provision. See 42 U.S.C.
§7475(a)(1). SIP development, as New Jersey quite correctly
points out, is an “arduous” task. NJ Br. 6. After SIP devel-
opment comes SIP implementation, which includes, among
other things, the issuance to individual facilities of operating
permits that specify those facilities’ emission limitations and
other compliance obligations. Then, there are the individual
PSD applications that regulators process under the prevail-
ing understanding of PSD requirements. Even on its less
aggressive reading of the PSD rules, for instance, ADEM
received, on average, 14 applications per year between 1997
and 2002 - each of which, as we have said, likely took quite
some time to process. See Presentation: PSD Permit Applica-
tions Received by Region 4 (Calendar Year), Annual Joint
EPA/State Enforcement Conference (Atlanta 2002).
Add to that the regulatory crush of EPA’s sweeping PSD
interpretation and the burden would become unsustainable.
24
Even after managing to educate themselves on the specifics
of the new PSD standards, state environmental regulators
would face a barrage of new permit applications concerning,
among other things, glue reformulations and ramp addi-
tions. See supra at 18. They would then scramble, on the
front end, to initiate dozens upon dozens of new reviews
and then, on the back end, to prosecute each and every
instance of noncompliance. Given their very limited re-
sources, it is almost inconceivable that many States would be
able to do the job, and, in any event, the explosion of bu-
reaucracy would be mind-boggling.°
The point is that this case is not about increasing permit-
ting loads at the margins. If Georgia-Pacific, for instance,
had been obliged to undergo pre-construction review for
each of iis 994 alleged “modifications,” the burden would
have overwhelmed both the company and state regulators.
The Clean Air Act, again, assigns front-line management
responsibility to the States, and the PSD program particu-
larly, given its complexity, indicates Congress’ intent to
structure an enforcement scheme that is sensitive to the
needs and capabilities of state regulators. EPA’s reading of
the PSD rules is anything but. On its view, primary state
control of Clean Air Act regulation would cease to be a “get
to” and would become, instead, a “have to.”
IV. EPA’s Litigating Position Has Fundamental Drawbacks
Even as a Matter of Environmental Policy.
We said at the outset that our disagreement with EPA
here principally concerns the legality and practicality of its
enforcement program, not the environmental policy under-
lying it. While that is true for the most part, there is an
important caveat.
9 EPA itself has recognized that the very aggressive NSR/ PSD interpreta-
tion that it is pursuing in these enforcement proceedings risks overtaxing
the “scarce resources” of “State and local reviewing authorities” and that
an hourly-rate-based reading would “reduce[] the reviewing authorities’
compliance and enforcement burden.” 70 Fed. Reg. 61,094 (Oct. 20, 2005).
25
This case, we should emphasize, does not pit white-
knight clean-air advocates against greedy polluters. It’s just
not that simple. In fact, there are important countervailing
consumer-related considerations to weigh against EPA’s
aggressive reading of the PSD rules, and, indeed, there are
very good clean-air reasons to oppose that reading.
1. Initially, and perhaps most obviously, there is the is-
sue of cost. There are two costs worth mentioning here.
One, as Justice Kennedy has quite rightly recognized, “is the
[permitting] process itself,” which, he notes, can require an
applicant to “spend up to $500,000.” Alaska, 540 U.S. at 515-
16 (Kennedy, J., dissenting). Another cost, far more signifi-
cant in dollar terms, is the technology itself. Under the
Clean Air Act's PSD provisions, a newly “constructed” (or
“modified,” see 42 U.S.C. §7479(2)(C)) source must ulti-
mately be equipped with “best available control technol-
ogy,” or “BACT.” 42 U.S.C. §7475(a)(4). BACT is, as its
name implies, the latest and greatest. The price tag can run
into the hundreds of millions of dollars per plant.
We have good reason to be concerned about cost, and it’s
not just because industry would have to spend more.
Rather, we are concerned that industry will pass on its own
increased costs to consumers in the form of higher, and in all
probability significantly higher, product prices, monthly bills,
and service fees.1° Of course, as a generic matter, States have
an interest in ensuring that their citizen-consumers can
afford basic goods and services. Thus, we worry that if, for
instance, even non-utility sources like saw, paper, and textile
mills had to be retrofitted with BACT, the prices for the
commodities those mills produce could skyrocket.
The States’ interest here is even more acute because this
case, like so many major PSD enforcement actions, involves
10 Alabama's PSC, for example, has authorized Alabama Power “to adjust
monthly billings to recover” costs associated with “compliance with
environmental laws, regulations, or other such mandates.” Alabama
Power Co. Petition for Adjustment of Rate CNP, Order at 1, Docket Nos.
18117, 18416 (Nov. 1, 2004).
26
a utility. That fact is significant in two related respects.
First, utilities have a statutory duty to provide the consum-
ing public with reliable service. See, e.g., Ala. Code §37-1-49
(“Every utility shall maintain its plant, facilities and equip-
ment in good operating condition .... Every utility shall
render adequate service to the public and shal] make such
reasonable improvements, extensions and enlargements of
its plants, facilities and equipment as may be necessary to
meet the growth and demand of the territory which it is
under the duty to serve.”). In order to meet that responsibil-
ity, utilities must from time to time repair and replace
deteriorating parts. Second, state Attorneys General have a
statutory obligation to protect the interests of utility rate-
payers. See, e.g., Ala. Code §37-1-16(a) (Attorney General
has authority to “intervenefe] in proceedings” before the
PSC “on behalf of the using and consuming public” in
matters pertaining to, among others, “rate applications, rate
changes and curtailments of service”). The States’ interest,
in sum, is in ensuring that their citizens have access to utility
services that are both reliable and affordable.
Accordingly, while clean air is a good, to be sure, it is not
a good that can, consistent with competing notions of
consumer protection, be pursued at all costs. Cf. Rodriguez v.
United States, 480 U.S. 522, 525-26 (1987) (“[N]o legislation
pursues its purposes at all costs.”). Particularly given the
multitude of other federal programs aimed at ensuring
cleaner air (NSR/PSD, as the EPA seems to acknowledge
here, is hardly the linchpin of the Clean Air Act's regulatory
apparatus!2), we think it quite likely that the harm brought
1 State Attorneys General take this obligation seriously and intervene on
behalf of rate-payers routinely. See, ¢.g., Alabama Power Co. Petition for
Revised Rate ECR Factor, Order at 1, Docket No. 18148 (Dec. 15, 2005)
(Attorney General intervened “to ensure that any rate increases are fair
and equitable to the consumer”).
22 EPA Br. 12 n3 (listing, among the “new programs that improve air
quality,” the Acid Rain Program, the NOx SIP Call, and the Clean Air
Interstate Rule (“CAIR”)). These new pollution-control programs, EPA
has said, “are more efficient than major NSR” and will more than offset
27
on by EPA’s enforcement-inspired reading of the PSD rules
- particularly for low- and middle-income families, who
may find themselves unable to afford next month’s power
bill - significantly outweighs the benefits.
2. More fundamentally, there are very good clean-air
reasons to oppose EPA’s position here. The sheer cost - in
money, time, and labor - of such an expansive pre-
construction permitting process, not to mention the installa-
tion of BACT at the culmination of that process, would
create an irresistible incentive for industry simply to avoid
repairs and replacements whenever and wherever possible,
and to continue running plants on old, deteriorating, and
environmentally-unfriendly components. Almost everyone
has been down this road at least once: Your old car emits
blue smoke, burns a quart of oil a month, and desperately
needs its piston rings replaced. Your mechanic tells you that
the job will run you $1800 and that , in any event, he can’t do
it for two weeks. What do you do? You just keep on driv-
ing, of course (and the blue smoke just keeps on pumping).
It's simpler, and cheaper, to keep pouring oil into the car.
So, too, here, rather than fixing broken parts - which under
EPA’s litigating position will trigger crippling expenses and
production delays - industry players will just keep their
plants running on inefficient, environmentally-unfriendly
parts.
EPA itself has acknowledged that running plants on de-
teriorating parts is an invitation to environmental trouble.
Indeed, the whole point of EPA’s recent NSR-reform rulemak-
ing initiative - part of which, of course, is to adopt prospec-
tively the very position we advance here - has been to avoid
encouraging plant owners to forego repairs in favor of
continued operation using sub-par equipment. See 70 Fed.
Reg. 61,083 (Oct. 20, 2005) (proposed rule adopting actual-to-
actual emission test); 68 Fed. Reg. 61,248 (Oct. 27, 2003) (rule
any marginal increase in emissions that might result from an hourly-rate-
based reading of the NSR modification rules. 70 Fed. Reg. 61,088.
28
ing “routine maintenance” exclusion), vacated, New
York, 443 F.3d 880. The reason, EPA has said, is that worn-
out parts often lead to “periods of startup, shutdown, and
malfunction,” which themselves “usually” entail “increased
emissions.” Id. at 61,251. As EPA has explained the prob-
lem, because the NSR/PSD permitting process is “time-
consuming and expensive” and “will likely result in a
requirement to retrofit an existing plant with state-of-the-art
pollution controls, which often is very costly and can present
significant technical challenges,” there is a very real risk that
a plant owner “may forego or curtail replacements that
would enhance the safe, reliable, or efficient operation of its
plant” Id. at 61,250; 70 Fed. Reg. 61,093 (same verbatim).
According to EPA, the solution - the sound environmental
solution, that is ~ is to remove the “perverse” incentive for
plant operators to limp by on deteriorating equipment. 68
Fed. Reg. 61,255; accord 70 Fed. Reg. 61,094 (object to “re-
move disincentives” to making changes that could, among
other things, enhance “environmental performance”).
The logic is compelling, and it applies precisely here. It
is impossible to square with the very different, max-PSD
policy that EPA is pursuing in these proceedings.
V. Section 307(b) Does Not Preclude Enforcement7
Proceeding Targets From Defending by Challenging
EPA’s Application of Clean Air Act Rules.
For two reasons, it seems to us clear that Section 307(b)’s
jurisdictional provision has no application here.
1. First, there is the plain text of the statute. Section
307(b)(1) requires that “petition[s] for review” challenging
(1) “promulgatfions]” of “nationally applicable regulations”
and (2) other “final action[s]” of EPA be filed in the D.C.
Circuit. 42 US.C. §7607(b)(1); accord id. §7607(e) (§307(b)
pertains to “regulations,” “orders of the Administrator”).
Section 307(b)(2) then states that any action “with respect to
which review could have been obtained” in a §307(b)(1)
petition for review shall not be subject to “judicial review” in
an enforcement proceeding. Id. §7607(b)(2). The question,
29
therefore, is whether Duke’s defensive argument that EPA
had misapplied the preexisting 1980 PSD rule would have
been proper under §307(b)(1).
It would not have been. A civil enforcement proceeding,
of course, is not a “petition for review” within the meaning
of §307(b)(1). No “promulgat[ion]” of any “regulation” is
being questioned here; the pertinent “regulation” here was
“promulgated” in 1980. Nor can EPA’s current interpreta-
tion (qua DOJ litigating position) concerning the 1980
regulation appropriately be considered a “final action.”
Final agency action, of course, has a stylized meaning in the
administrative-law context; to qualify, an agency’s pro-
nouncement must, at a minimum, “’mark the consummation
of [its] decisionmaking process.” Whitman v. American
Trucking Ass’ns, 531 U.S. 457, 478 (2001) (quoting Bennett v.
Spear, 520 U.S. 1 4, 178 (1997)). Particularly given EF A’s
flip-flopping interpretations of the 1980 PSD rule, its current
litigating position surely does not make the grade.
_ Petitioners’ and their amici’s jurisdictional analysis is,
with respect, based on a caricature of §307(b) rather than on
a careful reading of its language. New Jersey, for instance,
asserts at one point that Congress “demand[ed]” in §307(b)
that “the federal minimum requirements” be reviewed
exclusively via petition for review in the D.C. Circuit. NJ Br.
8. But that is not at all what §307(b) says; it speaks, instead,
solely in terms of “promulgatfions],” “regulation{s],” and
“final action{s].” Edging closer to §307(b)’s text, EPA and
other amici stake their argument on the assertion that the
Fourth Circuit’s decision here “effectively invalidates the PSD
regulations” themselves and thus triggers §307(b). EPA Br.
29, 31 (emphasis added); see also, e.g., NY Br. 4 (“effectively
invalidates”). That argument saddles the adverb with more
than it can bear. It depends on the premise that there is only
one reading of the PSD regulation that is even plausible -
namely, to require PSD review based solely on activity that
causes an hours-of-operation increase - and concludes that
any disagreement with that reading renders the regulation
itself a dead letter. As we have shown, however, any
ok, Oe
current assertion that the rule ust be understood to incor-
porate an hours-of-operation trigger is in ihe teeth of EPA’s
own vacillation on the issue. At the end of the day, the fact
remains that Duke’s argument here comes in defense to an
enforcement action that EPA itself initiated in North Caro-
lina. Duke’s defense entails only a challenge to EPA’s
application of the 1980 PSD rule to it, not a frontal assault on
the validity of the 1980 rule itself. This is not a §307(b) case.
2. Plain language aside, petitioners’ and EPA’s reading
of §307(b) would beget either grave unfairness, judicial
chaos, or both. It simply cannot be the law that where, as
here, EPA institutes a civil-enforcement proceeding in a local
district court, the targeted defendant is left with the
Hobson's choice of either (1) rolling over, not defending
itself, and accepting an adverse judgment or (2) instituting
an entirely separate and parallel action in the D.C. Circuit.
Surely, instead, when EPA itself decides to bring suit against
a plant operator in Alabama, for instance, that operator is
entitled to defend itself in Alabama, without cluttering the
court system with a duplicate action in Washington, D.C.
Cf. Adamo Wrecking Co. v. United States, 434 U.S. 275, 285
(1978) (§307(b) does not prevent criminal-enforcement target
from defending itself, so long as court does not invalidate
EPA’s “promulgatfion]” or the “regulation” itself).
The point is that any anti-forum-shopping policy that
might underlie §307(b), see EPA Br. 18, has absolutely no
application to an enforcement-action target like Duke. Here,
by contrast, the shoe is on the other foot. Recently, in Alaska, —
this Court emphasized that EPA may not seek to “achieve an
unfair advantage through its choice of litigation forum.” 540
US. at 493. Petitioners’ and EPA’s casual reading of §307(b)
~ which allows EPA to sue but forbids the target to defend ~
would encourage EPA to do just that.
CONCLUSION
For the foregoing reasons, this Court should affirm the
court of appeals’ judgment.
September 15, 2006
31
Respectfully submitted,
Troy King
Attorney General
Kevin C. Newsom
Solicitor General
Counsel of Record *
Robert D. Tambling
Chief, Environmental Division
STATE OF ALABAMA
Office of the Attorney General
11 South Union Street
Montgomery, AL 36130-0152
(334) 242-7401
Olivia Rowell
General Counsel
ALABAMA DEPARTMENT OF
ENVIRONMENTAL MGMT.
1400 Coliseum Blvd. »
Montgomery, AL 36110
(334) 271-7858
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