Amicus Curiae Brief — Chicago v. Environmental Defense Fund
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No. 92-1639
In the Supreme Court of the United States
OCTOBER TERM, 1993
THE CITy OF CHICAGO, ET AL... PETITIONERS
VS.
ENVIRONMENTAL DEFENSE FUND, INC... ET AL.
ON WRIT OF CERTIORARI
TO THE UNITED STATES COURT OF APPEALS
FOR THE SEVENTH CIRCUIT
BRIEF FOR THE UNITED STATES
AS AMICUS CURIAE SUPPORTING PETITIONERS
Drew S. Days, Ill
Solicitor General
MYLES E. FLINT
GERALD H. YAMADA Acting Assistant Attorney General
Acting General Counsel LAWRENCE G. WALLACI
LISA K. FRIEDMAN Deputy Solicitor General
Associate General Counsel preppy P. MINFAR
LAWRENCE E. STARFIELD Assistant to the Solicitor General
Assistant General Counsel py ayy ©. Sut TON
THOMAS H. BEISSWENGER M. ALIck THURSTON
Attorney Attorneys
Environmental Protection Department of Justice
Agency ; Washington, D.C. 20530
Washington, D.C. 20460 (202) 514-2217
BEST AVAILABLE COPY)s
QUESTION PRESENTED
Whether Section 3001(i) of the Resource Conservation
and Recovery Act of 1976, 42 U.S.C. 6921(i), exempts a
resource recovery facility’s municipal waste combustion
ash from regulation as a hazardous waste under Subtitle C
of that Act.
(I)
TABLE OF CONTENTS
Page
pueevent OF the United States .................... -
esi ccs ceseeceevens 2
I S
Argument:
EPA’s interpretation of Section 3001(i) is entitled
ec so cecccucvdevess eee y
A. Section 3001(i) is ambiguous with respect to
regulation of MWC ash................... y
B. EPA's interpretation of Section 3001{i) is
ce ceeeees 16
Ne ccc eedeecececees 28
TABLE OF AUTHORITIES
Cases:
American Hospital Ass'n vy. NLRB, 11S. Ct. 1839
ee i ci nancecesesecs 23
Bowen vy. Georgetown University Hospital, 488
rr . . wise eceeeces avn ee
Burlington Truck Lines, Inc. v. United States, 37\
cs occ eteccsceecees 25
Chevron U.S.A. Inc. v. Natural Resources Defense
Council, Inc., 467 U.S. 837 (1984) 2.0... 8, 11, 16, 17,
18, 20, 21, 22, 23, 28
City of Chicago v. Environmental Defense Fund,
a 8
Commodity Futures Trading Comm'n vy. Schor,
ns ccc cccccececece 20
Cottage Savings Ass'n ¥. Commissioner of Internal
Revenue, 111 S. Ct. 1803 (1991) 0.6... 20
Department of the Treasury v. FLRA, 494 U.S.
ES 17
(111)
IV
Cases — Continued:
Environmental Defense Fund vy. EPA, 852 F.2d
1316 (D.C. Cir. 1988), cert. denied, 489 U.S.
SOT Re ae ee ee
Environmental Defense Fund, Inc. v. Wheelabrator
Technologies, Inc., 725 &. Supp. 758 (S.D.N_Y.
1989), aff'd, 931 F.2d 211 (2d Cir.), cert. denied,
See es ED oc Kk GRCER SN eabbaeteess 7,
FDIC \. Philadelphia Gear Corp., 476 U.S. 426
SEE i hrdoo ease ee ais ak be wn ka ano
Good Samaritan Hospital y. Shalala, 113 S. Ct.
EE V0.6 8 hae x00 445 Chee eKen 16, 17, 18,
International Ass'n of Bridge Workers, Local 3 \.
NLRB, 843 F.2d 770 (3d Cir.), cert. denied, 480
Os Re a ete eek cei a Se wae nen
Lorillard v. Pons, 434 U.S. 575 (1978)... 00.2...
Mead Corp. v. Tilley, 490 U.S. 714 (1989) 000...
\Vlesa berde Constr. Co. \. Northern Cal. District
Council of Laborers, 861 F.2d 1124 (9th Cir.
Dt ccheatounausannsscesadsecdneehestwwns
Motor Vehicle Mfrs. Ass'n vy. State Farm Mutual
Auto. Ins. Co., 463 U.S. 29 (1983) 20000... 23.
NLRB vy. Curtin Matheson Scientific, Inc., 494
SE, Fe EE 6 dua casachaseuasetuceetchuss
NLRB. lron Workers, 434.U.S. 335 (1978)...
NLRB vy. United Food & Commercial Workers
Union, Local 23, 484 U.S. 112 (1987). 0.2... ..
Paulev \. BethEnergyv Mines, Inc., (ANS. Ct. 2524
GE 5 0.0esberescdetateceseneavens 16, 17-18,
Pension Ben. Guar. Corp. ». LTV Corp., 496
Se ee EE foro es oe a ae ea
Permian Basin Area Rate Cases, 390 U.S. 747
MR ee Ab AP see Ree pe
Sierra Club vy. U.S. Environmental Protection
Agency, 992 F.2d 337 (D.C. Cir. 1993) ........
Page
14,
20-
”7
~—s
tv
Cases — Continued: Page
Sullivan v. Everhart, 494 U.S. 83 (1990) ......... 16, 18
Traynor v. Turnage, 485 U.S. 535 (1988) ......... 20
United States v. Alaska, 112 S. Ct. 1606(1992) .... 16, 17
United States v. Gaubert, 111 S. Ct. 1267 (1991) .. 27
United States v. Shimer, 367 U.S. 374 (1961)... .. 21
Statutes and regulations:
Clean Air Act Amendments of 1990, Pub. L. No.
i ah eesaeue 14
I a a awe 14
Hazardous and Solid Waste Amendments of 1984,
Pub. L. No. 98-616, 98 Stat. 3221 ............. 3
of Bo 8: ASR rrr
Resource Conservation and Recovery Act of 1976,
ee ee PS ogo cacncccavinsceevese 2
§ 1004(7), 42 U.S.C. 6903(7) ............... 20
§ 1004(34), 42 U.S.C. 6903(34) ............. 20
§§ 3001-3018, 42 U.S.C. 6921-6939 ......... 2
op 8 8 8 ol RR A eee P 2
Be OE al en passim
§ 3001(if2), 42 U.S.C. 692112)... 2 2... 10
en a ai a le oo 2
SD ooo sec teau cue ean 2
2 ee ek oe Shae 2
§ 4010(c), 42 U.S.C. 6949a(c) ... 2... ee, 25
iat 5
ee rk hs i a ore 11
40 C.F.R.:
es i a ee i de ae 25, 26
Pt. 261:
Section 261.4(b)(1) ......... 3, 4, 10, 19, 20, 21
A eee eer eed ee ee 2
i se aca St ie 19
Miscellaneous:
AWD Technologies, Municipal Waste Combus-
tion, Ash and Leachate Characterization: Mono-
fill— Fourth Year Study, Woodburn Monofill,
Woodburn, Oregon (March 1992) ............
Clark Byse, Judicial Review of Administrative
Interpretation of Statutes; An Analysis of
Chevron’s Step Two, 2 Administrative L.J. 255
th aan ie wed ath nawee he aeeeee oS
Characterization of Municipal Solid Waste in the
United States: 1992 Update (EPA July 1992)...
45 Fed. Reg. (1980):
PP cixbncectucctsusbhessexnsvasess
i, FMD oc cess ccccescccccocennas
St: cccdnauccsvassencosacesses Oy OMS
9° Serr rrr rr Tree late bene es
50 Fed. Reg. (1985):
UE bb eewcs ness cekcenasuveceseessess
ie bo freer ere re
DPM catch shnehes cecnscdsenevetesess
86 Fed. Reg. (1991):
EE cha es ood ecbans se eabeads eee tan
DD ovens ccvotbiccvsin because sveuy es
H.R. 424, 103d Cong., Ist Sess. (1993) ..........
H.R. 2017, 103d Cong., Ist Sess. (1993) .........
H.R. 2488, 103d Cong., Ist Sess. (1993) ...
S. Levy, Municipal Waste Combustion Inventory
CE, Pe GUE bccn sbetesesceveseensaee es
Page
Vil
Miscellaneous — Continued:
Municipal Incinerator Ash: Hearing on H.R. 2517,
4255, and 4357 Before the Subcomm. on Trans-
portation, Tourism, and Hazardous Materials of
the House Comm. on Energy and Commerce,
Se Gs Ge EE wb o's es ue eeeséecas
Regulation of Municipal Solid Waste Incinerators:
Hearings on H.R. 2162 Before the Subcomm. on
Transportation and Hazardous Materials of the
House Comm. on Energy and Commerce, \0\st
Sed Sl es EE i cacecceneeuabes use hts
Resource Conservation and Recovery Act — Over-
sight: Hearings Before the Subcomm. on Haz-
ardous Wastes and Toxic Substances of the
Senate Comm. on Environment and Public
Works, 100th Cong., Ist Sess. (1987) .........
Results of U.S. EPA Research on Municipal Waste
Combustion, Otfice of Research & Develop-
ment, Cincinnati, Ohio (EPA March 1993,
DE c-tucucheskcconeeeu wk enee toe een east s
S. Rep. No. 284, 98th Cong., Ist Sess. (1983)
S. Rep. No. 301, 102d Cong., 2d Sess. (1992)
is s Oe
Page
13, 14
13-14
Jn the Supreme Court of the United States
OCTOBER TERM, 1993
No. 92-1639
TH! “ITY OF CHICAGO, ET AL., PETITIONERS
VS.
ENVIRONMENTAL DEFENSE FUND, INC., ET AI
ON WRIT OF CERTIORARI
TO THE UNITED STATES COURT OF APPEALS
FOR THE SEVENTH CIRCUIT
BRIEF FOR THE UNITED STATES
AS AMICUS CURIAE SUPPORTING PETITIONERS
INTEREST OF THE UNITED STATES
The United States plays a leading role through the En-
vironmental Protection Agency (EPA) in implementing
and administering federal environmental laws, including
the Resource Conservation and Recovery Act of 1976, 42
U.S.C. 6901 et seq. EPA addressed the statutory question
at issue here through a directive from its prior Ad-
ministrator to the EPA Regional Administrators, and that
directive remains in effect.
STATEMENT
Petitioners City of Chicago and its mayor operate a
municipal incinerator that burns solid waste and recovers
energy, leaving a residue of municipal waste combustion
(1)
2
(MWC) ash that is deposited in a landfill. Respondents
Environmental Defense Fund, Inc., ef a/. (EDF) brought
this action against petitioners alleging ‘hat they were
violating provisions of the Resource Co iservation and
Recovery Act of 1976 (RCRA), 42 U.S.C. 6901 ef seq., by
failing to dispose of the MWC ash in accordance with the
hazardous waste management requirements of RCRA
Subtitle C, 42 U.S.C. 6921-6939. The United States
District Court for the Northern District of Illinois granted
Summary judgment for petitioners, ruling that RCRA Sec-
tion 3001(i), 42 U.S.C. 6921(i), exempts the ash residue
from Subtitle C regulation. See Pet. App. 22a-37a. A
divided court of appeals reversed. /d. at Sa-2la. This
Court vacated that judgment and remanded the case for
reconsideration in light of a directive that the Administra-
tor of the EPA had recently issued to the EPA Regional
Administrators. On remand, the court of appeals
reinstated its prior judgment. /d. at la-4a
1. RCRA is a comprehensive enviro: nental statute
that, among other things, empowers EPA to regulate
hazardous wastes from “cradle to grave.” Environmental
Defense Fund v. EPA, 852 F.2d 1316, 1318 (D.C. Cir.
1988), cert. denied, 489 U.S. 1011 (1989). Subtitle C of
RCRA requires EPA to identify and list hazardous wastes,
§ 3001, 42 U.S.C. 6921, and to promulgate standards
governing hazardous waste generators and transporters,
$§ 3002, 3003, 42 U.S.C. 6922, 6923, and owners and
operators of hazardous waste treatment, storage, and dis-
posal facilities, § 3004, 42 U.S.C. 6924. EPA has directed
hazardous waste generators to comply with handling,
recordkeeping, storage, and monitoring requirements
when they treat, store, or arrange for transportation or
disposal of hazardous waste. See 40 C.F.R. Pt. 262.
In 1980, EPA issued regulations, pursuant to Section
3001 of RCRA, identifying and listing certain solid wastes
3
as hazardous wastes. See 45 Fed. Reg. 33,084. Based on
the agency’s interpretation of Congress’s intent, EPA ex-
cluded various solid wastes that might otherwise be treated
as hazardous waste from regulation under Subtitle C. See
id. at 33,096-33,097. EPA specifically provided a “house-
hold waste” exclusion, stating in relevant part:
The following solid wastes are not hazardous
wastes:
(1) Household waste, including household waste
that has been collected, transported, stored, treated,
disposed, recovered (e.g., refuse-derived fuel) or re-
used. “Household waste” means any waste material
(including garbage, trash and sanitary wastes in septic
tanks) derived from households (including single and
multiple residences, hotels and motels).
Id. at 33,120 (codified as amended at 40 C.F.R.
261.4(b)(1) (1982)). EPA stated that the exclusion would
extend to waste residues remaining after treatment, such
as incinerator ash. 45 Fed. Reg. 33,099 (1980). See Pet.
App. 25a-26a.
Four years later, Congress enacted the Hazardous and
Solid Waste Amendments of 1984, Pub. L. No. 98-616, 98
Stat. 3221, which revised and supplemented RCRA in
various respects. That Act (§ 213, 98 Stat. 3241) added
Section 3001(i), entitled “Clarification of household waste
exclusion.” 42 U.S.C. 6921(i). Section 3001(i) states:
A resource recovery facility recovering energy from
the mass burning of municipal solid waste shall not be
deemed to be treating, storing, disposing of, or other-
wise managing hazardous wastes for the purposes of
regulation under this subchapter, if —
(1) such facility —
(A) receives and burns only —
4
(1) household waste (from single and
multiple dwellings, hotels, motels, and
other residential sources), and
(ii) solid waste from commercial or
industrial sources that does not contain
hazardous waste identified or listed
under this section, and
(B) does not accept hazardous wastes
identified or listed under this section, and
(2) the owner or operator of such facility has
established contractual requirements or other ap-
propriate notification or inspection procedures
to assure that hazardous wastes are not received
at or burned in such facility.
42 U.S.C. 6921(i). Shortly thereafter, EPA revised its
regulation containing the household waste exclusion. 50
Fed. Reg. 28,702 (1985). EPA retained its original regu-
latory language, but added the language of Section 3001(i)
virtually verbatim. 40 C.F.R. 261.4(b)(1). See Pet. App.
26a-27a.
*. Since 1971, petitioner City of Chicago has owned
and operated a resource recovery incinerator, the North-
west Waste-to-Energy Facility. The facility burns approxi-
mately 350,000 tons of solid waste each year, amounting
to about 14% of the City’s solid waste, and produces
energy that is used within the facility and is sold to other
companies. The City has disposed of the combustion resi-
due — 110,000 to 140,000 tons of MWC ash per year —at a
landfill in Three Oaks, Michigan. Prior to this suit, the
City, like many other municipalities, did not manage
MWC ash as a RCRA Subtitle C hazardous waste. Pet.
App. Sa-7a, 23a.'
' As of 1991, approximately 150 facilities incinerated municipal
solid waste in a resource recovery facility. S. Levy, Municipal Waste
5
In 1988, EDF filed a complaint against petitioners under
the citizen suit provisions of RCRA, § 7002, 42 U.S.C.
6972, alleging that petitioners were violating provisions of
RCRA and EPA’s RCRA regulations governing the
management of hazardous waste. According to EDF, the
MWC ash from the Northwest Waste-to-Energy Facility
contained sufficient levels of lead and cadmium to subject
the residue to regulation as a hazardous waste under
RCRA Subtitle C. Petitioners responded that RCRA Sec-
tion 3001(i) nevertheless excluded the MWC ash from Sub-
title C requirements. The parties filed cross-motions for
summary judgment contesting the application of Section
3001(i). Pet. App. Sa-7a, 22a-24a.
EDF claimed that although Section 3001(i) exempted
petitioners fror RCRA Subtitle C requirements related to
“treating, stot.ug, disposing of, or otherwise managing
hazardous wastes,” 42 U.S.C. 6921(i), it did not exempt
petitioners from Subtitle C requirements related to genera-
tion of a distinct waste product, the MWC ash. Petitioners
responded that Section 3001(i)’s reference to “disposing
of, or otherwise managing hazardous wastes” exempted
from Subtitle C requirements the entire process of inciner-
ating the waste in a resource recovery facility, including
management of the ash residue. Pet. App. 7a, 24a,
27a-28a.
The district court agreed with petitioners that RCRA
Section 3001(i) exempts MWC ash produced at resource
recovery facilities from regulation as hazardous waste.
Pet. App. 7a, 24a-32a. The court denied petitioners’ mo-
Combustion Inventory 1 (EPA July 1992). In 1990, those facilities
burned in aggregate about 29.7 million tons of municipal solid waste
out of an estimated 195.7 million tons generated. Characterization of
Municipal Solid Waste in the United States: 1992 Update 3-2 (EPA
July 1992). See also Pet. 3-4.
6
tion for summary judgment, however, and allowed EDF
to engage in discovery on whether the Chicago facility ade-
quately met Section 3001(i)’s provisions prohibiting the
facility from accepting commercial and industrial hazar-
dous wastes. Pet. App. 7a, 32a-33a. EDF subsequently
stipulated that it would not contest the adequacy of the
facility’s compliance with those prohibitions and that it
would not oppose petitioners’ renewed motion for sum-
mary judgment, which the court granted. See id. at 7a-8a,
34a-37a.
3. The court of appeals reversed. As a preliminary
matter, the court rejected petitioners’ claim that inter-
vening legislation had rendered the matter moot. Pet.
App. 8a-9a. Turning to the merits, the court observed that
petitioners and EDF both relied on the “plain words of
section 3001(i)” and that “EPA’s interpretation and the
legislative history of the statute do little to resolve this
stand-off.” /d. at 10a-lla. See id. at 10a-18a (analyzing
those sources). The court ultimately chose to rely on “what
the statute actually says.” /d. at 18a.
The court reasoned that Section 3001(i) “mentions ‘the
treating, storing, disposing of or otherwise managing’ of
the household and commercial waste, but fails to include
among these activities generating a different waste prod-
uct entirely.” Pet. App. 18a. The court examined the
Statutory definitions of the quoted terms and ruled that
they “exclude ‘generation,’ which is separately defined as
‘the act or process of producing hazardous waste.’ 42
U.S.C. § 6903(6).” Jd. at 19a. It concluded:
There is no overlap whatsoever, then, between haz-
ardous waste “management” and hazardous waste
“generation.” It follows, therefore, that if the
language of the exclusion is limited to “management”
activities of resource recovery facilities, “generating”
activities are subject to regulation.
-
Ibid. The court accordingly held that “ash generated from
the incinerators of municipal resource recovery facilities is
subject to regulation as a hazardous waste under Subtitle
C of RCRA.” 7d. at 20a.
Judge Ripple dissented. He stated that the court should
affirm the judgment for the reasons set forth in Environ-
mental Defense Fund, Inc. v. Wheelabrator Technologies,
Inc., 725 F. Supp. 758 (S.D.N.Y. 1989), aff’d, 931 F.2d
211 (2d Cir.), cert. denied, 112 S. Ct. 453 (1991), which
held that MWC ash from resource recovery facilities is ex-
empt from regulation under Subtitle C. Pet. App. 21a.?
4. The City of Chicago petitioned for a writ of cer-
tiorari to resolve the conflict between the decisions of the
Second and Seventh Circuits. Pet. in No. 91-1328. EDF
agreed that the conflict should be resolved by this Court
and did not oppose the petition. Resp. Br. in No. 91-1328.
The Court thereafter issued an order inviting the Solicitor
General to present the views of the United States. On
September 18, 1992, while that invitation to the Solicitor
General was outstanding, EPA Administrator William
Reilly issued a memorandum to EPA Regional Admini-
Strators setting out EPA’s interpretation of Section
3001(i). Pet. App. 4la-49a. The Reilly memorandum
directed the Regional Administrators to treat MWC ash as
exempt from hazardous waste regulation under Subtitle C
of RCRA. I/bid. Thereafter, the Solicitor General sug-
gested that the Court grant the petition, vacate the deci-
sion and remand the case to the Seventh Circuit for further
consideration in light of EPA’s directive. U.S. Amicus Br.
in No. 91-1328. This Court followed that course and
? Because of the apparent conflict with the Wheelabrator decision,
the court of appeals’ opinion was circulated among all active circuit
judges prior to release. No judge recommended rehearing en banc. See
Pet. App. Sa n.*
a
8
returned the case to the Seventh Circuit. City of Chicago
v. Environmental Defense Fund, 113 S. Ct. 486 (1992).
5. After requesting and receiving statements of posi-
tions from petitioners and EDF, the court of appeals re-
instated its previous decision. The majority held that the
Reilly memorandum did not affect its analysis, because
the statute’s plain language was dispositive. Pet. App. 2a.
Judge Ripple again dissented. He stated that an agency has
an obligation to review and insure the reasonableness of its
interpretations On a continuing basis. Judge Ripple con-
cluded that Administrator Reilly’s review of the “ad-
mittedly ambiguous issue” and his reassessrent of the
agency’s “early pronouncements” were responsible agency
actions and deserved “deferential review.” Jd. at 4a.
SUMMARY OF ARGUMENT
The United States submits that Section 3001(i) of RCRA
is ambiguous with respect to regulation of MWC ash.
Although petitioners and EDF both invoke the “plain
language” of Section 3001(i), the statute does not speak
directly to the issue presented here. Indeed, EPA, which is
charged with administering RCRA, has grappled with that
issue since the statute’s enactment and has repeatedly
urged Congress to clarify the matter. At the same time, all
of the courts that have addressed the issue (except the
divided panel below) have acknowledged that the statute is
ambiguous. In these circumstances, the Court should give
deference to “a reasonable interpretation made by the ad-
ministrator of an agency.” Chevron U.S.A. Inc. v.
Natural Resources Defense Council, Inc., 467 U.S. 837,
844 (1984).
Administrator Reilly formally articulated EPA’s inter-
pretation in his 1992 directive to the Regional Administra-
9
tors, and that directive remains in force. The Court should
therefore defer to the reasoned analysis contained therein.
The directive sets out an interpretation that is consistent
with the text and legislative history of Section 3001(i), that
reconciles the statute and the agency’s regulatory scheme,
and that takes into account important policy and technical
considerations that are within EPA’s special expertise.
Deference is no less appropriate merely because the Ad-
ministrator’s construction is not the only reasonable inter-
pretation, it has evolved over time, and it could be revised
again in light of further technological or policy con-
siderations.
ARGUMENT
EPA’S INTERPRETATION OF SECTION 3001(i)
IS ENTITLED TO DEFERENCE
A. Section 3001(i) Is Ambiguous With Respect To Regulation
Of MWC Ash.
1. Petitioners and EDF each have contended through-
out this litigation that the plain language of Section 3001(i)
supports their respective positions. See Pet. App. 10a-1 1a.
They are able to rely on the same text to support contra-
dictory conclusions, because the statutory language is am-
biguous with respect to the specific question at issue. Sec-
tion 3001(i) states in relevant part:
A resource recovery facility recovering energy from
the mass burning of municipal solid waste shall not be
deemed to be treating, storing, disposing of, or other-
wise managing hazardous wastes for the purposes of
regulation under this subchapter if [certain conditions
are satisfied].
42 U.S.C. 6921(i). That provision, which is captioned as a
“clarification” of EPA’s pre-existing household waste ex-
10
clusion, is amenable to at least two different construc-
tions.
On the one hand, the provision can plausibly be inter-
preted to mean that if a facility is one that “recover[s]
energy from the mass burning of municipal solid waste”
and it satisfies the prescribed conditions, then the facility
as a whole is entitled to a regulatory exemption with
respect to any activity that, in the absence of the exemp-
tion, could constitute “treating, storing, disposing of, or
otherwise managing hazardous wastes.” 42 U.S.C. 6921(i).
Under that construction, EPA’s household waste exclu-
sion, set out at 40 C.F.R. 261.4(b)(1), would continue to
apply to the incineration residues, notwithstanding the
facility’s commingling of “household” and non-hazardous
“commercial or industrial” waste. The facility would enjoy
an exemption from RCRA Subtitle C regulation for ac-
tions taken in “treating, storing, disposing of, or otherwise
managing” both the incoming waste streams and the
MWC ash, which would continue to be subject to the
household waste exclusion even after leaving the facility.
On the other hand, Section 3001(i) can be construed in a
more restrictive sense to mean that the discrete aspects of
the facility’s energy recovery process specifically refer-
enced in the statute—treatment, storage, disposal, and
other management activities—do not include a non-
referenced activity — such as the “generation” of hazardous
waste. The facility would enjoy an exemption from RCRA
Subtitle C regulation when “treating, storing, disposing
of, or otherwise managing” any hazardous waste products
that are present in the incoming waste streams, despite
contractual controls established by the owner/operator of
the facility. See 42 U.S.C. 6921(i)(2). But the facility
would be subject to regulation under RCRA Subtitle C if
the incineration process generates a new product —
MWC ash—that qualifies as a hazardous waste.
2. Although one may debate the relative merits of the
competing constructions, both are plausible and consistent
with the statutory text. At bottom, “Congress has not
directly addressed the precise question at issue” — whether
the household waste exclusion, as clarified by Section
3001(i), applies to MWC ash. Chevron U.S.C. Inc. v.
Natural Resources Defense Council, Inc., 467 U.S. 837,
842 (1984). Indeed, the ambiguity in Section 3001(i) of
RCRA is not unlike the one that this Court encountered in
Chevron, where the question was whether the Clean Air
Act’s provisions regulating new or modified major sta-
tionary sources, 42 U.S.C. 7502(b)(6), should be applied
on a plantwide or a component-by-component basis. See
467 U.S. at 839-840. As in Chevron, EPA has considered
the matter “not in a sterile textual vacuum, but in the con-
text of implementing policy decisions in a technical and
complex arena.” /d. at 863. And as in Chevron, EPA’s in-
terpretation has consequently evolved over time.
When EPA promulgated its 1980 household waste ex-
clusion, it clearly envisioned that the regulatory exclusion
would exempt incineration residue from Subtitle C regula-
tion. EPA stated in the preamble to that regulation that it
was excluding the entire household waste stream from
regulation, observing:
Since household waste is excluded in all phases of its
. management, residues remaining after treatment
(e.g., incineration, thermal treatment) are not subject
to regulation as hazardous waste. * * *
45 Fed. Reg. 33,099 (1980). EPA explained that such
wastes, however, “must be transported, stored, treated
and disposed of in accord with applicable State and
federal requirements concerning management of solid
waste (including any requirements specified in regulations
under Subtitle D of RCRA).” Jbid.
12
Five years later, when EPA amended the household
waste exclusion in response to Congress’s enactment of
Section 3001(i), EPA expressed doubt whether MWC ash
should be excluded. EPA stated in the preamble to the
amended regulation:
The statute is silent as to whether hazardous
residues from burning combined household and non-
household, non-hazardous waste are hazardous
waste. These residues would be hazardous wastes
under present EPA regulations if they exhibited a
characteristic [of hazardous waste]. The legislative
history does not directly address this question,
although the Senate report can be read as enunciating
a general policy of nonregulation of these resource
recovery facilities if they carefully scrutinize their in-
coming wastes. On the other hand, residues from bur-
ning could, in theory, exhibit a characteristic of
hazardous waste even if no hazardous wastes are
burned, for example, if toxic metals become concen-
trated in the ash. Thus, the requirement of scrutiny of
incoming wastes would not assure non-hazardousness
of the residues.
50 Fed. Reg. 28,725-28,726 (1985). The agency continued:
EPA believes that the principal purpose of section
3001 [i] was to prevent resource recovery facilities that
may inadvertently burn hazardous waste, despite
good faith efforts to avoid such a result, from becom-
ing subject to the Subtitle C regulations. EPA does
not see in this provision an intent to exempt the
regulation of incinerator ash from the burning of
non-hazardous waste in resource recovery facilities if
the ash routinely exhibits a characteristic of hazard-
ous waste.
Id. at 28,726. See Pet. App. 30a n.4. Although those pre-
amble passages are somewhat equivocal, they have been
13
widely viewed as indicating that if MWC ash “exhibits a
characteristic of hazardous waste,” ibid., the ash is subject
to RCRA’s Subtitle C requirements. °
Since 1985, EPA officials have suggested that, in that
respect, the analysis contained in the 1985 regulatory pre-
amble may be incorrect and have urged Congress to clarify
its intent. Congress subsequently included a provision in
’ EPA also stated, however, that the Hazardous and Solid Waste
Amendments do not “impose new regulatory burdens on resource
recovery facilities that burn household and other non-hazardous
waste, and the Agency has no plans to impose additional responsi-
bilities on these facilities.” 50 Fed. Reg. 28,726 (1985). EPA deter-
mined that “any future additional regulation of their residues would
have to await consideration of the important technical and policy
issues that would be posed in the event serious questions arose about
the residues.” /bid.
* In 1987, EPA’s Assistant Administrator for the Office of Solid
Waste and Emergency Response stated to a Senate subcommittee that
“[t}he Agency has reexamined that [1985] interpretation and now con-
cludes that it may have been in error. The Agency believes that the
language and legislative history of Section 300i(i) were probably in-
tended to exclude these ash residues from regulation under Subtitle
C.” Resource Conservation and Recovery Act — Oversight: Hearings
Before the Subcomm. on Hazardous Wastes and Toxic Substances of
the Senate Comm. on Environment and Public Works, \00th Cong.,
Ist Sess. 427-428 (1987). See Pet. App. I4a-iSa. In 1988, the Ad-
ministrator testified to a House subcommtittee that “there is ambiguity
within the law and I think the law should be clarified,” but he also in-
dicated that the Agency would not take action to clarify its interpreta-
tion of the law out of deference to Congress, which was at the time
considering legislation to amend the provision. Municipal Incinerator
Ash: Hearing on H.R. 2517, 4255, and 4357 Before the Subcomm. on
Transportation, Tourism, and Hazardous Materials of the House
Comm. on Energy and Commerce, 100th Cong., 2d Sess. 72 (1988). In
1989, EPA’s Director of the Office of Solid Waste stated to a House
subcommittee that EPA continued to follow the 1985 interpretation,
but she noted that there is “substantial controversy surrounding that
interpretation,” “the law is ambiguous given it is silent with regard to
treatment of ash under [Section 3001(i)],” and “it needs to be clari-
14
the Clean Air Act Amendments of 1990, Pub. L. No.
101-549, 104 Stat. 2399, stating:
For a period of 2 years [until November 15, 1992]
* * * ash from solid waste incineration units burning
municipal waste shall not be regulated by the Admini-
strator of the Environmental Protection Agency pur-
suant to section 3001 of the Solid Waste Disposal Act.
$ 306, 104 Stat. 2584. Since enactment of that “mora-
torium” provision, however, Congress has taken no action
to clarify whether it intends MWC ash to be exempt per-
manently from Subtitle C regulation, and has, as a body,
remained silent on this controversy.°
In light of the considerable uncertainty surrounding the
issue, the imminent termination of the two-year mora-
fied.” Regulation of Municipal Solid Waste Incinerators: Hearings on
H.R. 2162 Before the Subcomm. on Transportation and Hazardous
Materials of the House Comm. on Energy and Commerce, \0\st
Cong., Ist Sess. 33 (1989). See Pet. App. 13a-l6a. See also
HW heelabrator, 725 F. Supp. at 767-768.
* In the past several years, Congress has considered various pro-
posals that would clarify how MWC ash should be regulated. In 1988,
Congress considered legislation that would have required specific
standards for facilities disposing of MWC ash. See 53 Fed. Reg.
33,314, 33,328 (1988). In 1988, a bill was introduced that would have
allowed disposal of MWC ash in certain RCRA Subtitle D landfills
which met additional requirements (the so-called “D Plus” approach).
See Municipal Incinerator Ash: Hearings on H.R. 2517, 4255, and
4357 Before the Subcomm. on Transportation, Tourism, and Hazar-
dous Materials of the House Comm. on Energy and Commerce, 100th
Cong., 2d Sess. 72 (1988). See also Pet. App. 12a-13a. In the session
that ended in 1992, Congress considered a bill that would have amend-
ed RCRA Subtitle D to establish a separate regulatory framework for
MWC ash. See S. Rep. No. 301, 102d Cong., 2d Sess. 56-60 (1992).
Various pertinent provisions have also been introduced in the current
session and are currently pending before Congress. See H.R. 424,
103d Cong., Ist Sess. (1993); H.R. 2017, 103d Cong., Ist Sess. (1993);
H.R. 2488, 103d Cong., Ist Sess. (1993).
15
\orium, and Congress’s failure to take legislative action,
EPA issued a policy directive to clarify the agency’s inter-
pretation of Section 3001(i). See Pet. App. 41a-49a. Ad-
ministrator Reilly’s September 1992 memorandum, which
was issued to all EPA Regional Administrators and made
publicly »vailable, announced EPA’s decision under Sec-
tion 3001(i) of RCRA “to treat ash generated from the
combustion of nonhazardous municipal solid waste at
resource recovery facilities * * * as exempt from hazard-
ous waste regulation under RCRA Subtitle C.” /d. at 41a.
That decision “supersede[d] the Agency’s earlier view of
section 3001(i) as not exempting MWC ash from hazard-
ous waste regulation.” /d. at 42a. The current Administra-
tor has not revised or revoked that directive, and it there-
fore remains in effect and continues to bind the Regional
Administrators.
As EPA’s experience demonstrates, Section 3001(i) is
amenable to more than one interpretation. Prior to the
court of appeals’ decision in this case, the courts that had
examined the issue had concluded —in accord witli the ex-
pert agency charged with administering the statute —that
the statutory language is ambiguous as to the issue pre-
sented here. See Pet. App. 24a; Wheelabrator, 725 F.
Supp. at 764, aff'd, 931 F.2d at 212. See also Pet. App. 4a
(Ripple, J., dissenting). The Seventh Circuit is the only
court to conclude that the statutory text is dispositive, and
that divided court’s reliance on the purported “plain
language” seemingly arises from the court’s own perplexity
in attempting to resolve the issue, rather than from any
compelling force in the statute’s words. Indeed, the court
conducted a preliminary analysis of the statute, its enact-
ment, and EPA’s implementation and stated:
What we have to work with here is a statute subject to
varying interpretations, a foggy legislative history, and
a waffling administrative agency. Where do we turn?
16
See Pet. App. 16a. The court then returned to the statu-
tory text and concluded, on second thought, that it should
adopt EDF’s “plain language” argument, relying in part on
“RCRA’s policy.” /d. at 18a-20a. But significantly, the
court simplified its task by ignoring the alternative “plain
language” argument — viz., petitioners are exempt because
the facility enjoys an exemption from RCRA Subtitle C
regulation for actions taken in “treating, storing, dispos-
ing of, or otherwise managing” both the incoming waste
streams and the outgoing MWC ash. 42 U.S.C. 6921(i).
At bottom, the adversaries in this case can each invoke
“plain language” in support of their competing interpreta-
tions, but neither can definitively refute the other party’s
construction. The court of appeals chose one “plain
language” argument in preference to another, but the fact
remains that Congress has not “directly spoken to” the
precise question presented in this case. Chevron, 467 U.S.
at 842. The statute ultimately is ambiguous with respect to
the issue presented here. Compare Rust v. Sullivan, 111 S.
Ct. 1759, 1767 (1991).
B. EPA's Interpretation Of Section 3001(i) Is Reasonable
1. This Court’s decision in Chevron supplies the
fundamental principle for resolving this case: A court in-
terpreting an ambiguous provision of a statute ad-
ministered by an agency must give deference to the
agency’s interpretation if that interpretation is
“reasonable.” Chevron, 467 U.S. at 844. See, e.g., Good
Samaritan Hospital v. Shalala, 113 S. Ct. 2151, 2159
(1993); United States v. Alaska, 112 S. Ct. 1606, 1610
(1992); Pauley v. BethEnergy Mines, Inc., 111 S. Ct. 2524,
2534 (1991); Rust v. Sullivan, 111 S. Ct. at 1767; Pension
Ben. Guar. Corp. v. LTV Corp., 496 U.S. 633, 647-648
(1990); Sullivan v. Everhart, 494 U.S. 83, 88-89 (1990);
Mead Corp. v. Tilley, 490 U.S. 714, 722 (1989).
17
As this Court has explained, “when an agency is charged
with administering a statute, part of the authority it re-
ceives is the power to give reasonable content to the
statute’s textual ambiguities.” Department of the Treasury
v. FLRA, 494 U.S. 922, 933 (1990). “That is a task infused
with judgment and discretion, requring the ‘accommoda-
tion of conflicting policies that were committed to the
agency’s care.’” Ibid. The principle of deference to ad-
ministrative interpretations
has been consistently followed by this Court when-
ever a decision as to the meaning or reach of a statute
has involved reconciling conflicting policies, and a
full understanding of the force of the statutory policy
in the given situation has depended upon more than
ordinary knowledge respecting the matters subjected
to agency regulations.
Chevron, 467 U.S. at 844 (citations omitted).
Administrator Reilly’s directive that Section 3001(i) ex-
empts MWC ash from RCRA Subtitle C regulation is the
expert agency’s currently operative interpretation of an
ambiguous provision of a complex statute. That directive
attempts to reconcile the text of Section 3001(i), its
legislative history, EPA’s pre-existing regulatory program,
and the underlying policies of RCRA, which include the
goals of protecting the environment and promoting
resource recovery from nonhazardous solid waste. See
Pet. App. 42a-49a. Under Chevron, the proper inquiry
now is whether the agency’s interpretation “is based on a
permissible construction of the statute.” 467 U.S. at
842-843. See Good Samaritan Hospital, 113 S. Ct. at 2156;
Alaska, 112 S. Ct. at 1610; Rust, 111 S. Ct. at 1759; LTV
Corp., 496 U.S. at 648; Mead Corp., 490 U.S. at 722.
To answer that inquiry, a court should examine whether
the agency’s interpretation is “reasonable,” Pauley, 111
18
S. Ct. at 2537, in the sense that it is “rational and con-
sistent with the statute.” Everhart, 494 U.S. at 89, quoting
NLRB vy. United Food & Commercial Workers Union,
Local 23, 484 U.S. 112, 123 (1987). As this Court recently
noted, “where the agency’s interpretation of a statute is at
least as plausible as competing ones, there is little, if any
reason not to defer to its construction.” Good Samaritan
Hospital, 113 S. Ct. at 2161. Indeed, that approach not
only gives proper respect to the agency’s congressionally
assigned function, but it also assigns the courts to their
proper role by directing disputes over policy to the
politically accountable branches of government. See
Chevron, 467 U.S. at 864-865. That approach is particu-
larly appropriate here, where the statutory provision
builds upon a pre-existing agency regulation.
2. EPA’s interpretation of Section 3001(i) is manifest-
ly rational. As the Reilly memorandum explains, Congress
enacted Section 3001(i) to clarify EPA’s 1980 household
waste exclusion, which exempted househcid waste from
Subtitle C regulation “in all phases of its management, [in-
cluding] residues remaining after treatment (e.g., incinera-
tion, thermal treatment).” 45 Fed. Reg. 33,099 (1980). See
Pet. App. 42a-43a. Section 3001(i) incontestably clarified
that when a resource recovery facility processes household
waste in combination with nonhazardous commercial and
industrial waste and in compliance with prescribed re-
quirements, the facility “shall not be deemed to be
treating, storing, disposing of, or otherwise managing
hazardous wastes.” 42 U.S.C. 6921(i). See Pet. App.
43a-44a. It is not unreasonable to conclude that this “clari-
fication” retains the basic thrust of EPA’s pre-existing
regulatory provision and continues to exempt the com-
bined household and nonhazardous commercial and in-
dustrial waste from regulation “in all phases of its manage-
19
ment,” including disposal of the resulting incineration
residues.°®
As the former Administrator’s memorandum explains,
his interpretation is entirely consistent with the statutory
text. See Pet. App. 42a-43a. Indeed, Section 3001(i)’s ex-
press provision that a qualifying resource recovery facility
“shall not be deemed to be treating, storing, disposing of,
or Otherwise managing hazardous wastes” reasonably sug-
gests that EPA’s household waste exclusion applies to all
facets of the facility’s operations, including incineration,
pre- and post-incineration storage, and disposal of
residues. The fact that Section 3001(i) fails to state that the
facility shall not be deemed to be “generating” hazardous
wastes (see Pet. App. 19a-20a) does not undermine that
conclusion. The absence of that term may simply reflect
Congress’s understanding that resource recovery opera-
tions involving conversion of solid waste to energy are
comprehensively described by the collective terms Con-
* It is helpful to understand how EPA’s RCRA regulations operate
in this setting. Under those regulations, a person who generates solid
waste “must determine if the waste is hazardous” by first “deter-
min{ing) if the waste is excluded from regulation under 40 CFR
261.4.” See 40 C.F.R. 262.11. A facility that incinerates waste, reduc-
ing it to ash, would find that “[hJousehold waste, including household
waste that has been * * * treated [e.g., reduced to ash]” is excluded
from regulation. 40 C.F.R. 261.4(b)(i). The question would arise,
however, whether the household waste exclusion continues to apply
when “household waste” is incinerated in combination with nonhaz-
ardous “commercial or industrial” waste. Section 3001(i) of
RCRA—which EPA codified virtually verbatim into 40 C.F.R.
261.4(b)(1)—clarifies that point. The municipal facility “shall not be
deemed to be treating, storing, disposing of, or otherwise managing
hazardous wastes” if the prescribed conditions are met. See 40 C.F.R.
261.4(b)(1). Thus, the household waste exclusion continues to apply,
and the resulting MWC ash remains exempt from hazardous waste
regulation.
20
gress used. See RCRA § 1004(7) and (34), 42 U.S.C.
6903(7) and (34) (defining hazardous waste management
and treatment).’ At most, Congress’s silence on that point
highlights the fact that Congress has “left a gap for the
agency to fill.” Chevron, 467 U.S. at 843-844. See Pet.
App. 44a n.2.
The Reilly memorandum’s interpretation of Section
3001(i) is especially plausible when the statute is viewed in
its legal context. When Congress acted, it presumably was
aware that EPA had interpreted the household waste ex-
clusion to apply to such waste “in all phases of its manage-
ment,” including disposal of incineration residues. See 45
Fed. Reg. 33,099 (1980).* Congress did not question or
overrule that interpretation when it clarified that the
household waste exclusion would apply to a resource re-
covery facility that burns commingled wastes, and it is
therefore reasonable for the Administrator to conclude
that Congress ratified that interpretation. See Cottage
Savings Ass’n v. Commissioner of Internal Revenue, 111
S. Ct. 1503, 1508 (1991); Traynor v. Turnage, 485 U.S.
535, 545-546 (1988); Commodity Futures Trading
Comm’n v. Schor, 478 U.S. 833, 845-846 (1986); FDIC v.
’ Significantly, Section 3001(i) employs terms similar to those that
EPA had employed in its prior regulatory exclusion. Compare RCRA
§ 3001(i), 42 U.S.C. 6921(i) (facility shall not be deemed to be
“treating, storing, disposing of, or otherwise managing hazardous
wastes”) with 40 C.F.R. 261.4(b)(1) (1982) (excluding household
waste, including waste “that has been collected, transported, stored,
treated, disposed, recovered (e.g., refuse-derived fuel) or reused”) and
45 Fed. Reg. 33,099 (1980) (excluding household waste “in all phases
of its management”).
* Cf. Lorillard v. Pons, 434 U.S. 575, 581 (1978) (“where, as here,
Congress adopts a new law incorporating sections of a prior law, Con-
gress normally can be presumed to have had knowledge of the inter-
pretation given to the incorporated law, at least insofar as it affects
the new statute”).
|
Philadelphia Gear Corp., 476 U.S. 426 (1985). And to the
extent the legislative history is relevant, it suggests that
Congress intended to retain EPA’s interpretation. S. Rep.
No. 284, 98th Cong., Ist Sess. 61 (1983). See Pet. App.
44a-46a & nn.2-3.
The Reilly memorandum also is consistent with the ob-
jectives Congress sought to achieve in enacting Section
3001(i)— protecting the environment and promoting re-
source recovery from nonhazardous solid waste. See Pet.
App. 46a-48a. As in Chevron, “Congress intended to ac-
commodate both interests, but did not do so itself on the
level of specificity presented by th[is] case[ ].” 467 U.S. at
865. Based on EPA’s scientific judgment and the safe-
guards the agency has instituted in implementing other
provisions of RCRA, Administrator Reilly determined
that those objectives “are best served by exempting MWC
ash from hazardous waste regulation.” Pet. App. 46a.
That determination rests on “significant expertise” and
“entail[s] the exercise of judgment grounded in policy con-
cerns.” Pauley, 111 S. Ct. at 2534. “In those circum-
stances, courts appropriately defer to the agency entrusted
by Congress to make such policy determinations.” /bid.
See Chevron, 467 U.S. at 844-845, quoting United States
v. Shimer, 367 U.S. 374, 382 (1961).°
* EDF has mistakenly suggested that this approach is “unworkable
and makes no sense,” because Section 3001(i) does not provide a
separate exemption for downstream parties that transport or dispose
of the MWC ash. See EDF Br. on Petition 12 n.8, 16 n.10. Under the
Administrator’s interpretation, the household waste exclusion con-
tinues to apply to a qualifying facility’s disposal products after they
leave the facility. This approach is consistent with the basic thrust of
the household waste exclusion, which Section 3001(i) was intended
merely to clarify, as applying to exempted waste “in all phases of its
22
3. As this Court’s decision in Chevron made clear,
deference is appropriate even if the agency has changed its
interpretation over time, provided that the agency supplies
a reasoned basis for the change. “The fact that the agency
has from time to time changed its interpretation * * *
does not * * * lead us to conclude that no deference
should be accorded the agency’s interpretation of the
Statute.” Chevron, 467 U.S. at 863. An agency’s consistent
adherence to a longstanding interpretation may provide an
additional reason for deference, but it is not a sine qua
non for respecting the agency’s views. Compare, e.g.,
Pauley, 111 S. Ct. at 2575 (citing a consistent agency prac-
tice), with Chevron, 467 U.S. at 865 (citing other factors
that support deference).
For example, it would provide no reason for a court to
reject an agency’s changed interpretation if practical ex-
perience or technological advances indicate that a revised
interpretation is more consonant with congressional in-
tent. Indeed, this Court recently ruled that an agency ad-
ministrator is not “estopped from changing a view she
believes to have been grounded upon a mistaken legal in-
terpretation.” Good Samaritan Hospital, 113 S. Ct. at
2161. As the Court explained:
“{Ajii administrative agency is not disqualified from
changing its mind; and when it does, the courts still sit
in review of the administrative decision and should
not approach the statutory construction issue de novo
and without regard to the administrative understand-
ing of the statutes.”
management,” including disposal of the resulting incineration
residues. See note 6, supra and accompanying text. Thus, a down-
Stream transporter or disposer may continue to rely on the household
waste exclusion when handling MWC ash.
23
lbid., quoting NLRB vy. Iron Workers, 434 U.S. 335, 351
(1978) (other citations omitted). To be sure, the Court sug-
gested that the weight that should be given to the agency’s
changed views “will depend on the facts of individual
cases.” 113 S. Ct. at 2161. But this Court has repeatedly
accorded deference where, as here, the agency provides a
reasoned justification for its changed position. E.¢., Rust,
111 S. Ct. at 1769; American Hospital Ass’n vy. NLRB, 111
S. Ct. 1539, 1546 (1991); Robertson v. Methow Valley
Citizens Council, 490 U.S. 332, 335-336 (1989).
EPA has consistently recognized that Section 3001(i) is
silent or ambiguous with respect to the issue presented in
this case. See pp. 11-15 supra. The agency’s contempo-
raneous interpretation of the 1985 rules codifying Section
3001(i) was replete with doubt as to Congress’s intent. See
50 Fed. Reg. 28,725-28,726 (1985). EPA has always
acknowedged that a statutory gap exists that must be
filled, and it has searched for the best means to do so. The
fact that the agency’s understanding has evolved over time
is nO reason to deny deference to the current interpretation
of the law in favor of the agency’s earlier, less seasoned ex-
plication.
Indeed, EPA should not be discouraged from continu-
ing to adjust its position as circumstances warrant. An
agency should revise its views as necessary to reflect new
learning that better informs the agency’s interpretation of
statutory provisions. As the Court has explained, “[a]n ini-
tial agency interpretation is not instantly carved in stone.”
Chevron, 467 U.S. at 863. Rather, the agency “must con-
sider varying interpretations and the wisdom of its policy
on a continuing basis.” Jd. at 863-864. Accord Rust. 111 S.
Ct. at 1769; NLRB v. Curtin Matheson Scientific, Inc.,
494 U.S. 775 (1990); Motor Vehicle Mfrs. Ass’n v. State
Farm Mutual Auto. Ins. Co., 463 U.S. 29, 42 (1983),
24
citing Permian Basin Area Rate Cases, 390 U.S. 747, 784
(1968).'°
To be sure, an agency changing its course—even if it
does not involve “rescinding a rule”—should “supply a
reasoned analysis for the change.” Motor Vehicle Mfrs.
Ass'n, 463 U.S. at 42. In accordance with that principle,
Administrator Reilly provided a reasoned explanation for
the new policy. His directive to the EPA Regional Ad-
ministrators explained that the interpretation is consistent
with the text and legislative history of Section 3001(i). See
Pet. App. 42a-43a. In addition, the directive addressed im-
portant policy considerations that are within EPA’s exper-
tise. Id. at 46a-49a.
The directive explained that resource recovery from
municipal solid waste “is an important component of
EPA’s integrated waste management approach” that can
“reduce the volume of waste that requires disposal” and
may result in “recovering significant amounts of energy.”
Pet. App. 47a-48a. The directive additionally noted that
EPA had recently promulgated new criteria for municipal
‘© Thus, the courts of appeals have quite correctly held that a ruling
by this Court upholding an agency’s interpretation as reasonable does
not preclude the agency from subsequently changing its interpretation
in light of additional knowledge or experience. See /nternational Ass'n
of Bridge Workers, Local 3 v. NLRB, 843 F.2d 770, 776 (3d Cir.),
cert. denied, 488 U.S. 889 (1988); cf. Mesa Verde Constr. Co. v.
Northern Cal. District Council of Laborers, 861 F.2d 1124, 1134-1136
(9th Cir. 1988). That approach is sound as an institutional matter. The
expert agency that administers the statute is best equipped to revisit
and fine tune reguiatory programs on a nationwide basis in light of
current knowledge, relieving Congress and the judiciary of the need
repeatedly to reassess the details of very complicated technical or
policy-laden matters. See Clark Byse, Judicial Review of Ad-
ministrative Interpretation of Statutes: An Analysis of Chevron’s Step
Two, 2 Administrative L.J. 255, 257-260 (1988).
a
25
solid waste landfills. 40 C.F.R. Pt. 258.'' Those criteria
contain many requirements that enhance the ability of
regulated landfills to contain and manage MWC ash safely:
The Part 258 criteria impose requirements on
municipal landfills that far exceed those previously
imposed, including more stringent location restric-
tions, facility design and operating criteria, ground-
water monitoring requirements, corrective action re-
quirements, financial assurance requirements, and
closure and post-closure requirements.
Pet. App. 46a-47a. The knowledge that EPA gained
through promulgation of the Part 258 criteria and the
changed circumstances led it to reevaluate previous policy
concerns and to conclude that “disposal of MWC ash in
municipal landfills subject to the Part 258 criteria will be
protective of human heath and the environment.” /d. at
47a & n.5.
Thus, Administrator Reilly reviewed the pertinent law,
evaluated the relevant policy considerations, applied the
available data, and articulated a satisfactory explanation
for his decision, providing a “ ‘rational connection be-
tween the facts found and the choice made.’ ” Motor Vehi-
cle Mfrs. Ass’n, 463 U.S. at 43, quoting Burlington Truck
Lines, Inc. v. United States, 371 U.S. 156, 168 (1962). His
analysis finds additional support in the rulemaking record
‘' EPA promulgated the Part 258 criteria in response to Section
4010(c) of RCRA, which directs EPA to reissue landfill criteria “for
facilities that may receive hazardous household wastes or hazardous
wastes from small quantity generators under [Section 3001(d)].” 42
U.S.C. 6949a(c). See Sierra Club vy. U.S. Environmental Protection
Agency, 992 F.2d 337 (D.C. Cir. 1993). The new Part 258 regulations
require landfills to be designed and operated to meet criteria
“necessary to protect human health and the environment,” taking into
consideration “the ‘practicable capability’ of [such] facilities.” See 56
Fed. Reg. 50,983 (1991).
26
of the Part 258 criteria, which details the scientific,
Statistical, and statutory analyses supporting promuiga-
tion of the new landfill requirements. See 40 C.F.R. Pt.
258, 56 Fed. Reg. 50,978 (1991).'?
4. Administrator Reilly’s directive has not been re-
pealed or superseded, and it therefore continues to state
EPA’s policy unless and until the agency revisits the issue.
Nevertheless, EDF urged and the court of appeals con-
cluded that the directive is not entitled to deference. They
have given two reasons—apart from their mistaken re-
liance on the purportedly “plain” language of the statute,
see pp. 9-16, supra—for disregarding the outstanding
agency interpretation. Neither is persuasive.
First, EDF has contended that Administrator Reilly’s
directive is not entitled to deference, because the directive
is comparable to an agency’s “convenient litigating posi-
tion.” Resp. Br. on Remand 6 n.2, quoting Bowen v.
Georgetown University Hospital, 488 U.S. 204, 212
(1988). See also EDF Br. on Petition 16. T'.at contention
is manifestly wrong. Administrator Reilly’s directive is a
formal interpretation by an agency head that establishes
current agency policy, has binding effect on subordinate
agency officials, and is therefore a legitimate source for
‘? EPA has conducted additional studies on MWC leachate, using
natural and synthetic lining materials commonly employed in the con-
struction of municipal solid waste landfill liners. Those studies in-
dicate that “with proper engineering considerations, carefully selected
materials can be expected to perform as designed.” Results of U.S.
EPA Research on Municipal Waste Combustion, Office of Research
and Development, Cincinnati, Ohio (EPA March 1993, Draft). In ad-
dition, EPA is conducting ongoing, in situ studies of leachate from
monofills receiving MWC ash. Those studies reveal concentrations of
relevant metals within allowable limits. See AWD Technologies,
Municipal Waste Combustion, Ash and Leachate Characterization:
Monofill— Fourth Year Study, Woodburn Monofill, Woodburn,
Oregon (March 1992).
27
Chevron deference. See Bowen, 488 U.S. at 212. Cf.
Alaska, 112 S. Ct. at 1618-1619, citing United States v.
Gaubert, 111 S. Ct. 1267, 1274 (1991) (agencies may estab-
lish policy “through administration of agency
programs”).'*
Second, the court of appeals concluded that Admini-
strator Reilly’s directive was not entitled to deference be-
cause EPA had changed its interpretation not just once,
but several times. See Pet. App. 2a (“EPA has changed its
view so often that it is no longer entitled to the deference
normally accorded an agency’s interpretation of the
statute it administers.”); see also id. at 16a (referring to
“[t]he see-sawing statements from the EPA”). That con-
clusion is erroneous as a factual matter. EPA has articu-
lated a formal agency position interpreting Section 3001(i)
only twice —in the preamble to the 1985 regulations and in
Administrator Reilly’s 1992 memorandum. Thus, the
agency has changed its position on the statute’s meaning
only once.'4
'* EDF cannot accurately compare the Administrator’s directive to
a mere pro hac vice argument from agency counsel that has no in-
dependent force. Indeed, EDF's citation to Bowen is particularly in-
apt, because EPA is not a party to this suit and has participated as
amicus curiae at this Court’s invitation. The fact that Administrator
Reilly issued his directive while this Court’s invitation was pending
provides no reason for denying deference. There is nothing inappro-
priate in an agency’s providing formal regulatory guidance concerning
issues that have given rise to litigation. Moreover, Administrator Reil-
ly had an independent reason for providing clarification, because the
congressional moratorium on agency regulation of MWC ash was
scheduled to expire on November 15, 1992. See p. 14, supra.
'* Statements that agency officials made to congressional commit-
tees advising the legislators of the agency’s concerns and requesting
clarification of Section 3001(i)’s ambiguous statutory language, see
p. 13, supra, obviously do not constitute formal changes in agency
policy.
28
But more fundamentally, a court is not entitled to ig-
nore an administrative agency’s interpretation simply be-
cause the agency has changed its mind—even if it has
changed its mind several times. Indeed, this Court’s deci-
sion in Chevron explicitly addresses that question:
The fact that the agency has from time to time
changed its interpretation * * * does not, as respond-
ents argue, lead us to conclude that no deference
should be accorded the agency’s interpretation of the
Statute.
467 U.S. at 863. The sole question is whether the Admini-
Strator has “amply justified his change of interpretation
with a ‘reasoned analysis.’ ” Rust, 111 S. Ct. at 1769. In
this case, Administrator Reilly provided just such an
analysis, and that currently outstanding interpretation is
entitled to deference.
CONCLUSION
The judgment of the court of appeals should be reversed.
Respectfully submitted.
Drew S. DAYS, Ill
Solicitor General
GERALD H. YAMADA MYLES E. FLINT
Acting General Counsel Acting Assistant Attorney General
LISA K. FRIEDMAN LAWRENCE G. WALLACE
Associate General Counsel Deputy Solicitor General
LAWRENCE E. STARFIELD JEFFREY P. MINEAR
Assistant General Counsel Assistant to the Solicitor General
THOMAS H. BEISSWENGER DAVID C. SHILTON
Attorney M. ALICE THURSTON
Environmental Protection Attorneys
Agency
AUGUST 1993
US GOVERNMENT PRINTING OFFICE 1993— 342.479/60336
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