31
March 2003
U.S.
Environmental Protection Agency
EPA
West (Air Docket)
1200
Pennsylvania Ave., N.W.
Room
B108, Mail Code: 6102T
Washington,
D.C. 20460
Re:
Docket ID No. A-2002-04
Ladies
and Gentlemen:
We
direct our comments to the proposed rule redefining Routine Maintenance,
Repair, and Replacement (RMRR). All of
us have experience in studying air pollution regulations and/or the health
effects caused by air pollution. Robert R.M. Verchick is Ruby M. Hulen
Professor of Law and Urban Affairs at the University of Missouri at Kansas City
(UMKC), where he teaches and writes about environmental regulation and
environmental justice. The other
contributors are J.D. candidates at UMKC, where they are studying environmental
issues; in addition some of these students have previous educational or
professional experience in the areas chemistry, public health, and industrial
chemical manufacturing. We offer these
comments on behalf of ourselves individually and on behalf the Black Law
Students Association at UMKC, the Environmental Law Society at UMKC, the Health
Law Society at UMKC, the Hispanic Law Students Association at UMKC, and the
Public Interest Law Association at UMKC.
Our comments are not intended
to reflect the views of UMKC School of Law, UMKC, or the University of Missouri
system.
The
New Source Review (NSR) program applies to the construction of new major
emitting industrial facilities and to existing facilities that make major
modifications that significantly increase pollution emissions. The program requires that new plants and
major modifications of existing plants obtain a permit before
construction. Such a permit will only be
issued if the new plant or major modification includes pollution control
measures that reflect the Best Available Control Technology for sources in
attainment areas and the Lowest Achievable Emissions Rate in nonattainment
areas.[1] The Clean Air Act (the “Act”) defines “new
source” to include existing sources that later undergo “modifications.”[2] A “modification” is “any physical change” or
“change in method of operation . . . which increases the amount of any air
pollutant emitted by such source.”[3] Courts have consistently read this definition
to mean exactly what it says: any change is a “modification” so long
as the change is physical and increases air pollution.[4]
The only exemption involves truly trivial changes representing “routine
maintenance, repair, and replacement.”
EPA created the exception to relieve itself of the impossible burden of
having to enforce new source requirements for even minimal repairs.[5] The Court of Appeals for the D.C. Circuit
validated the routine maintenance exemption on the grounds that its effects
were de minimus.[6] Thus, so long as EPA construes this exemption
narrowly, the rule is legal.
The
new proposed rule abandons EPA’s narrow, case-by-case determinations of de minimus maintenance exemptions in
favor of a much more liberal program that automatically exempts certain
categories of modification by defining them as RMRR per se. These per se categories eschew any reference
to trivial or de minimus effects and
instead appear designed only to relieve regulators of case-by-case
analyses. One per se category would exclude from new regulation all projects that
fall within an as yet undetermined “annual allowance” to be defined by total
expenditures as a percentage of capital cost.
A second per se category would exclude from new regulation all projects involving
the replacement of existing equipment with functionally equivalent new
equipment.
Because
it abandons the required de minimus
standard, the proposed rule stretches EPA’s original maintenance exemption
beyond the breaking point. In addition
the proposed rule will increase pollution, intensifying damaging health and environmental
effects. The possibility of increased
air pollution also creates the possibility of increased environmental justice
concerns. Finally, the proposed rule also hamstrings
state and local governments in protecting their local airsheds, a result at
odds with this Administration’s own preference for federalism and local
autonomy. We take each objection in
turn.
A. The Proposed Rule Is Inconsistent with
the Clean Air Act.
The
proposed rule undercuts both the plain meaning of the Clean Air Act and
Congress’s underlying intent. It
breaches the plain meaning because “modification” is literally defined as “any physical change” that “increases the
amount of any air pollutant.”[7] Courts take this language literally,
permitting exceptions only in de minimus situations.[8] The proposed exemptions require no limits on new pollutants, as both the
text and the courts require. Instead,
the EPA focuses on expenditure/capital cost ratios and functional equivalency
of added equipment, elements which appear nowhere
in section 7411’s definition of “modification.”
The
proposed exemptions breach Congress’s intent because the proposed rule will increase air pollution and significantly
delay any future application of
modern pollution-control technology to existing plants. It is already widely acknowledged that the
Administration’s “Clear Skies” initiative, taken as a whole, would allow 36%
more nitrogen, 50% more sulfur dioxide and 190% more mercury into the air by
2018 than would existing regulations.[9] The proposed maintenance rule, which would
applies to roughly 17,000 plants nation-wide, would contribute to this problem.[10]
Specifically,
the proposed rule’s “annual allowance” would lead to increases in criteria pollutants in some attainment and
non-attainment areas. The proposed
rule’s “functional equivalency” exemption would allow indefinite upgrading of
existing equipment without ever requiring new pollution controls.
1.
The “Annual Allowance” Increases Pollution.
The “annual allowance” exemption
threatens to increase criteria pollutants by encouraging newer plants to
augment their facilities in ways that increase production and pollution. The
reason lies in EPA’s preference for across-the-board capital-cost
formulae. To see why, consider the
exemption’s effect on two competing plants, an older existing plant and a newer
existing plant. The older source will
have a lower replacement cost and therefore a lower RMRR allowance. The newer source will have a higher
replacement cost and therefore a higher RMRR allowance. The older source will have relatively higher
maintenance costs than the newer one with similar production levels, since its
equipment is older and requires more frequent repair.
If the older source has greater
maintenance requirements but a smaller RMRR allowance, it may use its entire
allowance for necessary retrofits.
Indeed, the most likely scenario is that it will “max-out” its allowance
and be required to submit to case-by-case review by the EPA. Meanwhile, the newer existing source, which
has a much lower maintenance requirement, will enjoy a surplus in its RMRR
allowance. This surplus creates an
incentive for the newer source to use its surplus allowance to augment its
production capacity and increase its
air emissions, knowing that such an increase—however—significant will not be subject to the most recent new
source standards. Some in the EPA have insisted the “annual
allowance” exemption is not intended to increase pollution and, in practice,
will not. If this is so, we urge EPA to honor this understanding by
inserting an explicit de minimus cap
on new emissions that occur in conjunction with RMRR.[11]
As the new source provisions make clear,
Congress never intended to permit non-de
minimus increases in pollution in non-attainment areas. Similarly, it did not intend significant
increases of pollutants in attainment areas.
(And neither per se category
prohibits even significant
increases.)
Even if the “annual allowance” exemption
did not up-end Congressional intent, it would still not relieve EPA of its
enforcement challenges—one of the touted advantages of the “annual allowance”
exemption. As pointed out, the older
existing plants (which make up the majority) will still require case-by-case
review by the EPA because the annual allowances, if calculated in relation to
capital cost, will seldom be enough to cover necessary repairs. Thus, case-by-case review will continue to
represent a significant proportion of EPA’s investigative and enforcement
work. This is appropriate; indeed, we
would like to see more case-by-case review.
EPA’s real challenge is not
that it has too much work, but that the current Administration has not provided
the Agency enough workers. Thus,
according to government records obtained through the Freedom of Information
Act, the number of EPA inspectors and enforcement officials was cut more than
12 percent last year.[12] Indeed, the current staffing at EPA’s Office
of Enforcement of Compliance Assurance is now the lowest since the government
began keeping records in 1996. The
“annual allowance” exemption cannot make up for this deficit.
2.
The “Functional Equivalence”Exemption Would Lead to Indefinite Upgrading and
More Pollution.
The “functional equivalence” exemption
would allow indefinite upgrading of existing equipment without new controls by
allowing facilities to replace different parts of a system incrementally over a
series of years without ever triggering new source review. This effect would undercut the intent of
Congress. Congress specifically adopted
new source standards with the understanding that they would lead to an
incremental “dying off” of older plants (retrofitted or not) and their later
replacement with more tightly regulated new facilities. By allowing operators to indefinitely prolong
the lives of older plants, the proposed rule would make it harder for new
plants to enter the market and compete, thus reversing the very effects (new plants replacing old plants)
Congress intended to pursue. The
preservation of older plants in this regulatory scheme virtually insures that
airsheds will be more polluted than would have been the case otherwise.
3. The Courts Will Not Defer to EPA’s
Judgment Where Such Legislative Opposition Exists.
Without an explicit cap on emissions
resulting from RMRR, the proposed rule would surely meet stiff resistance in
the federal courts. The proposed rule’s
inconsistency with the Act is so fundamental that the courts’ traditional
deference to agency rulemaking would not save it. In Chevron,
USA, Inc. v. Natural Resources Defense Council, Inc.,[13] the U.S. Supreme Court made clear that
where an agency rule violates a statute’s unambiguous meaning, it is invalid.
The Supreme Court decision, Chicago v. Environmental Defense Fund,[14]
indicates three points to be considered that are relevant here: (1) the statute’s “plain meaning,” (2) the
neighboring sections of the statute (3) and the stated goals of the statute.[15] As discussed earlier, the statute’s plain
meaning could not be clearer: the
proscription of an increase of “any” pollutant means just that. The Act’s neighboring provisions, which
require state implementation plans to reduce
pollutants in non-attainment areas and to prevent
increases in attainment areas corroborates the plain meaning of section
7411. As for the Act’s purpose, Congress
declared its objective was to “protect public health and welfare . . . preserve
protect and enhance air quality . . . [and] preservation of existing air
resources.”[16] The proposed rule is inconsistent with these
objectives.
B. Because the Proposed Rule Will Increase
Pollution, It Will Intensify Damaging Health and Environmental Effects
Thirty thousand Americans already
die early deaths because of air pollution in todays’s skies.[17] The EPA bears a legal and ethical responsibility
to prevent further such damage tomorrow.
Exposure to pollution is damaging to the human body. Studies show that multiple or consecutive
exposures to pollution lead to serious health concerns, and even disease. The proposed changes to the Clean Air Act
will likely increase pollution, especially in the form of particulate emissions
from coal-fired plants. Among the most
harmful to humans are nitrogen oxides (NOx) and sulfur dioxides (SO2). Power plants that emit these particulates are
adding to an ozone layer that lies close to the ground, commonly referred to as
smog. The combination of smog and
particulate matter causes detrimental health effects.
The list of medical problems
associated with airborne pollution is exhaustive. The respiratory system is the most commonly
attacked area of the body, but pollution effects are not limited to the
lungs. Complaints associated with
pollution exposure include: asthma, bronchitis, eye irritation, colds, stomach
irritation, suffocation, claustrophobia, allergies, decrease in body energy and
efficiency, and decreased lung capacity and function.[18]
Exposure to particulate pollution in
great enough amounts or over an extended period of time can turn complaints
into serious medical problems and diseases.
The most common diseases are heart and lung disease, but stomach cancer,
emphysema, and heart attacks have also been linked to pollution
inhalation.
Statistical data collected from
patients exposed to pollution are frightening.
Chronic exposure to particulate pollution can shorten life by up to
three years, lower lung capacity by 15 to 20 percent, and damage the lungs
roughly equal to smoking half a pack of cigarettes a day.[19] Risk of early death increases 15 to 17
percent where particulate matter pollution creates smog.[20] Lung disease alone kills 335,000 Americans
yearly, and deaths from asthma related attacks have doubled between 1980 and
1993.[21] Lung, heart, and other bodily diseases
associated with inhaled pollution result in deterioration of the total body
system, and possibly death.
The effect that smog based pollution
has on children is of primary importance.
Ground level ozone is responsible for 15,000 premature deaths and one
million lung function problems in children annually.[22] Children have different oxygen and blood
requirements than adults so the effects of pollution on their bodies are even
more devastating. Since children are
still growing and generally more active than adults, their body systems require
more blood and oxygen than that of an adult.[23] Children breathe on average 50 percent more
air per pound of body weight than adults.[24] Asthma has become the leading chronic illness
in children, as well as the leading cause for hospital admissions among the
nation’s youth. The world is not ours;
we are merely borrowing it from our kids.
The proposed changes to the Act will likely increase pollution levels
and result in our leaving a dirtier planet with air that is harder to breathe
for our children.
Smog is generally viewed as an urban city haze and is common in areas of industrialization. Common effects on the planet include decreases in crop production, increases in acid rain, and devastating effects on plants and wildlife. Acid rain is responsible for rendering lakes and streams too acidic to support plant and fish life, aids in the destruction of monuments and buildings, impairs visibility, and kills many of the large canopy trees in the North Eastern states.[25]
Killing the large canopy trees creates special concerns in the Northeast, as they are responsible for producing the oxygen that we breathe. High concentrations of ground level ozone make it harder for trees to produce the oxygen people need and makes it harder for humans to inhale what oxygen they do produce. Ground level ozone is responsible for increased radiation exposure from the sun. Smog, under certain conditions, has the effect of intensifying the amount of radiation that hits the earth and trapping it there, creating perilous effects on plants, animals, and humans.
C. The Possibility of Increased Air
Pollution and Health Problems Creates the Possiblity of Increased Environmental
Justice Concerns.
Under the Executive Order on
Environmental Justice, the EPA is required to “make achieving environmental
justice part of its mission” and to consider the effects of its policies and
decisions on the health and environment of low-income or minority
neighborhoods.[26] Over the last twenty years, ample evidence
throughout the United States suggests that the brunt of environmental
burdens—including air pollution and geographic proximity to industrial
facilities—are borne by the poor and people of color.[27]
Given market forces (which direct
polluting facilities to poorer areas), current housing patterns (in which
people of color are more likely to live near many kinds of polluting facility),
and the realities of political power (in which the poor and people of color
often have less ability to successfully lobby their local governments for
protection), one can expect that any environmental fallout from the proposed
rule will be visited to a disproportionate degree on the poor and on people of
color—individuals who, incidentally, are the least likely to have knowledge
about the risks they face and the medical resources to address them.
Empirical data support this view. Consider the states of New York,
Pennsylvania, and New Jersey, which, in addition to seven other states, have
challenged EPA’s proposed rule in federal court.
In New York’s Albany County, the ratio of
air-polluting facilities (e.g., facilities that emit criteria pollutants)
located near minority residents as compared to those located near white
residents is 2.45 to 1.[28] The ratio of such facilities near “low
income” and “high income” residents is 2.46 to 1.[29]
In Pennsylvania’s Allegheny County, the
ratio of air-polluting facilities located near minority residents as compared
to those located near white residents is 2.44 to 1.[30] The ratio of such facilities between “low
income” and “high income” residents is 2.05 to 1.[31]
In New Jersey’s Camden County, the ratio
of air-polluting facilities located near minority residents as compared to
those located near white residents is 5.38 to 1.[32] The ratio of such facilities between “low
income” and “high income” residents is 1.18 to 1.[33]
Given this clear knowledge of air pollution inequalities based on race and
class, the EPA should avoid any rule that would impose additional health risks
on members of these vulnerable groups.
D. The Proposed Rule Hamstrings State and
Local Governments in Protecting their Local Airsheds, a Result at Odds with
this Administration’s Own Preference for Federalism and Local Autonomy.
The
proposed rule is particularly damaging to state and local autonomy, a principle
the Bush Administration purports to hold in high esteem. This is because as the per se exemptions work to increase air pollution, states (and their
local governments) will have fewer options in meeting the federally-mandated
National Ambient Air Quality Standards (NAAQS) and will be even more threatened
by spill-over pollution coming from neighboring states.
1. States Will Have Fewer Options in
Meeting the NAAQS.
In general, it is the states not the federal government that bears
the responsibility of insuring compliance with the NAAQS.[34] The imposition of this burden is justified on
the grounds that states know best how to achieve an maintain air quality in the
local airshed. Thus Congress and the EPA
have traditionally given states broad flexibility in their regulations as long
as the states meet the air standards.
The proposed per se exemptions
deprive states one of the strongest tools they have in controlling
emissions: federally uniform
restrictions on modifications to existing sources. Without such restrictions, states will then
be pushed to allow maintenance modifications that increase pollution and to
offset those increases by imposing tighter restrictions on some other emission
sources. This will be exceedingly
difficult, given that existing stationary sources are responsible for so much
of states’ air pollution problem. The
result, we fear, is that the number of non-attainment areas will simply
increase, exposing states to even more federal reprisals for air pollution
problems that the federal government helped to make worse.
2. States Will Be Even More Threatened by
Spill-Over Pollution Coming from Neighboring States.
Many downwind states are unable to meet their NAAQS because
upwind power plants disregard their pollution’s transboundary effects. This lack of respect for state boundaries
limits the ability of downwind states to maintain clean air and thus intrudes
upon their political autonomy. The
course of action provided to the states, either through section 126 petitions
or individual state litigation, has led to governmental and judicial backlog,
ineffective results in reducing air pollution, and a decrease in state
resources. Because the proposed rule
would increase pollution and weaken state’s ability to comply with the NAAQS,
one should expect transboundary air-pollution disputes to grow even uglier, an
event that would further erode state and local autonomy.
Transboundary pollution involves the deposition of particulate matter in a state other than where it was emitted. It is more difficult for Northeast states to meet their NAAQS requirements because wind patterns carry particulates eastward.
a. Section
126 Petitions.
Section 126 of the Clean Air Act
provides downwind states a measure of recourse against upwind states that are
responsible for their failure to meet the requirements of NAAQS. A state that does not meet its emission cap
can file a section 126 petition with the EPA.
Section 126 petitions are often met with frustration and unsatisfactory
results.
The
EPA and U.S. Department of Justice (“DOJ”) have limited time and resources to
handle the continually growing Section 126 petitions that have been filed by
various Northeastern states. These
section 126 petitions require the EPA to test power plants in upwind states for
higher than allowed emissions or require plants to submit emissions data. This is a long and complicated process that
potentially involves multiple states and over 300 power plants.[35]
In the past, the EPA has been
reluctant to intervene in transboundary pollution issues between states,
preferring states to work issues out on their own.[36] Often negotiations between states break down
because of the high standards in the Northeast and low standards the Midwest
and South want to adopt.[37] The proposed regulations would allow power plants
in the Midwest and South to have greater emissions, making it even harder for
the Northeastern states to meet their NAAQS caps. This intrudes upon the autonomy of
Northeastern states and limits their ability to negotiate.
The number of section 126 petitions has
increased over the last couple of years and has resulted in litigation to
address ever-growing problems between states.
Several suits, brought by the EPA and enforced by the DOJ, have ended in
awards or settlements against power plants in upwind states that cause
nonattainment in downwind states.
Unfortunately, the new revisions proposed by the EPA impede litigation,
and the rollback the revisions allow cause current settlements to be nullified.
The new regulations will result in a
greater number of section 126 petitions being filed and bury the EPA further in
litigation. This would be a considerable
draw on resources and does not deter violating power companies and upwind
states from emitting too much pollution.
b. Lawsuits Brought by States.
Frustrated
by the section 126 process, some states have pooled resources to sue violating
power plants. Northeastern states, such
as New York, began suing individual plants.
Some of these cases have been settled, but with the potential new
regulations, the current litigation is on hold.
Industry lawyers have urged EPA to make its proposed rule retroactive so
that power companies can avoid liability under these suits. Allowing
retroactive regulations would be disastrous for the downwind states and would
further erode their ability to protect the health and welfare of their
citizens.
E. Conclusion.
For these reasons, we urge the EPA
to reconsider its proposed rule on RMRR in its entirety. At the very least, we urge that the EPA add a
de minimus cap on increases of air pollution permitted for RMRR
modifications and that the rule’s effects not be made retroactive.
Thank
you for considering our comments.
Sincerely,
Robert R.M.
Verchick
Ruby M. Hulen
Professor of Law and Urban Affairs
University of
Missouri at Kansas City (UMKC)
5100 Rockhill
Road
Kansas City, MO
64113-2499
tel: 816.235.2381
verchickr@umkc.edu
Jessica M.
Agnelly
J.D. Candidate,
UMKC
Kristine Freeman
J.D. Candidate
UMKC
Michael Hundley
J.D. Candidate
UMKC
Cathy L. Legan
J.D. Candidate
UMKC
Andrew S. Leroy
J.D. Candidate
UMKC
Liu, Jin
J.D. Candidate
UMKC
Christopher S.
Moberg
J.D. Candidate
UMKC
and
Lauren Syler
J.D. Candidate
UMKC
on behalf of
themselves and the following organizations:
The Black Law
Students Association, UMKC
The
Environmental Law Society, UMKC
The Health Law
Society, UMKC
The Hispanic Law
Students Association, UMKC
The Public
Interest Law Association, UMKC
[1] 42 U.S.C. §§ 7475(a)(4) and 7503(a)(2).
[2] 42 U.S.C. § 7411(a).
[3] Id.
[4] See Alabama Power Co. v. Costle, 636 F.2d 323, 400 (D.C. Cir. 1979) (“’modification’ is nowhere limited to physical changes exceeding a certain magnitude”); Wisconsin Electric Power Plant Co. v. Reilly, 893 F.2d 901, 905 (7th Cir. 1990) (“the potential reach of these modifications is apparent: the most trivial activities—the replacement of leaky pipes, for example—may trigger the modification provisions if the change results in an increase in the emissions of a facility”).
[5] See 40 C.F.R.§52.21(b)(2)(iii).
[6] Alabama Power, 636 F.2d at 360-61.
[7] 42 U.S.C. § 7411(a)(emphasis added).
[8] Alabama Power, 636 F.2d at 360-61.
[9] See, e.g., Jim O’Neil, Bush Misleads on Air Pollution, The Oregonian, Feb. 1, 2003.
[10] See Editorial, Clean Politics, Philadelphia
Inquirer, Feb. 3, 2003; National
Resources Defense Council,, Clean Air & Energy: Bush Record available at <http://www.nrdc.org/bushrecord/airenergy_powerplants.asp#1196.>NRDC, Record”)
[11] One might respond by saying that such a cap would reduce the regulatory efficiency of the per se categories by again requiring attention to individual context. This response ignores two points. First, case-by-case review of older facilities will still be necessary even with the “annual allowance,” as we discuss later. Second, efficiency, while an appropriate goal, does not trump the plain meaning and intent of the Act.
[12] NRDC, Record, supra note 10.
[13] 467 U.S. 837 (1984).
[14] 511 U.S. 328.
[15] Id. at 332-39.
[16] 42 U.S.C. § 7041 (2003).
[17] National Resources Defense Council,, Clean Air & Energy: Air pollution: In Brief available at <http://www.nrdc.org/air/pollution/fnsr.asp#1>.
[18] W. David Slawson, The Right to Protection from Air Pollution, 59 S. Cal. L. Rev. 672, 684-87, 695 (1986).
[19] Public Health Report 1997; 112; 366-67.
[20] Id.
[21] Id.
[22] Vickie Patton, Court Affirms Historic Clean Air Standards, available at <www.enviromentaldefense.org/article.cfm?contentid=1868> .
[23] Public Health Report 1997; 112; 366-67
[24] Id.
[25] Attorney General Sorrell Joins AGs from Northeast States to Press Bush Administration For Clean Air, <www.state.vt.us/atg/press01082002.htm>(Jan. 8, 2002).
[26] Executive Order No. 12898, 3 C.F.R. 859 (1995); see generally, Denis Binder, Robert R.M. Verchick, et al., A Survey of Federal Agency Response to President Clinton’s Executive Order No. 12898 on Environmental Justice, 31 Environmental Law Reporter 11133 (2001).
[27] See Robert R.M. Verchick, The Commerce Clause, Environmental Justice, and the Interstate Garbage Wars, 70 S. Cal. L. Rev. 1239, 1289-90nn.277-70 (citing multiple sources).
[28] Environmental Defense Fund (“EDF”), Scorecard, available at <http://www.scorecard.org/community/ej-summary.tcl?fips_county_code=36001#dist >(using data from the 1990 U.S. Census).
[29] Id.
[30] EDF, Scorecard, available at <http://www.scorecard.org/community/ej-summary.tcl?fips_county_code=42003#dist >(using data from the 1990 U.S. Census).
[31] Id.
[32] EDF, Scorecard, available at <http://www.scorecard.org/community/ej-summary.tcl?fips_county_code=34007#dist >(using data from the 1990 U.S. Census).
[33] Id.
[34] 42 U.S.C. §§ 7404; 7410.
[35] Appalachian Power Co. v. EPA, 249 F.3d 1032, * (2001).
[36] Christina C. Caplan, The Failure of Current Legal and Regulatory Mechanism to Control Interstate Ozone Transport: The Need for New National Legislation, 28 Ecology L.Q. 169, 187 (2001).
[37] Id.