Appendix — Northeastern Pharmaceutical & Chemical Co. v. United States
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yu Of Bet
No. | JOSEPH F. SPANIOL, JR.
abi.
IN THE
Supreme Court of the United States
OCTOBER TERM, 1986
NORTHEASTERN PHARMACEUTICAL AND CHEMICAL
COMPANY, INC., ef a/.,
Petitioner,
VS.
UNITED STATES OF AMERICA,
Respondent.
APPENDIX TO PETITION FOR WRIT OF
CERTIORARI TO THE UNITED STATES COURT OF
APPEALS FOR THE EIGHTH CIRCUIT
TED L. PERRYMAN*
JOHN L. WALKER
ROBERTS, PERRYMAN & BOMKAMP, P.C.
1015 Locust Street, Suite 700
St. Louis, Missouri 63101
(314) 421-1850
Attorneys for Petitioners
* Counsel of Record
St. Louis Law Printing Co., Inc., 411 No. Tenth Street 63101 314-231-4477
TABLE OF CONTENTS
Page
Appendix A - Opinion of Court of Appeals ........... A-1l
Appendix B - Judgment of Court of Appeals.......... A-48
Appendix C - Order of Court of Appeals denying peti-
PIL ook pu cue cvewvssonses A-49
Appendix D - Memorandum Opinion of District Court - A-50
Appendix E - Order for final Judgment .............. A-109
Appendix F - Order of District Court denying motion to
alter or amend judgment.............. A-112
Appendix G - Notice of Appeal ..................... A-114
Appendix H - Notice of Cross-Appeal ............... A-II15
Appendix I - Constitutional and statutory provisions
EE cs SCEN ar Oded aba Skea Nea A-116
APPENDIX A
UNITED STATES COURT OF APPEALS
FOR THE EIGHTH CIRCUIT
No. 84-1837
Lnited States of America,
Appellee,
¥.
Northeastern Pharmaceutical & Chemical Co., Inc.,
a Dissolved Delaware Corporation, Edwin Michaels
and John W. Lee,
Appellants.
Ronald Mills and Syntex Agribusiness, Inc.
No. 84-1853
United States of America,
Appellant,
v.
Northeastern Pharmaceutical & Chemica! Co., Inc.,
a Dissolved Delaware Corporation, Edwin Michaels
and John W. Lee,
Appellees,
Ronald Mills and Syntex Agribusiness, Inc.
Appeal and Cross-appeal from
the United States District Court
for the Western District of Missouri
—A-2—.
Submitted: March 25, 1985
Filed: December 31, 1986
Before McMILLIAN, JOHN R. GIBSON and BOWMAN,
Circuit Judges.
McMILLIAN, Circuit Judge.
Northeastern Pharmaceutical & Chemica! Co. (NEPACCO),
Edwin Michaels and John W. Lee appeal from a final judgment
entered in the District Court' for the Western District of
Missouri finding them and Ronald Mills jointly and severally
liable for response costs incurred by the government after
December 11, 1980, and all future response costs relative to the
cleanup of the Denney farm site that are not inconsistent with
the national contingency plan (NCP) pursuant to §§ 104, 107 of
the Comprehensive Environmental Response, Compensation,
and Liability Act of 1980 (CERCLA), 42 U.S.C.n§§ 9604, 9607
(appeal No. 84-1837). For reversal, appellants argue the district
court erred in (1) applying CERCLA retroactively, (2) finding
Michaels and Lee individually liable, (3) failing to dismiss
NEPACCO as a party defendant, (4) awarding response costs
absent affirmative proof that the response costs were consistent
with the NCP, (5) refusing to reduce the award of response costs
by the amount of a prior settlement, and (6) denying appellants
a jury trial.
The United States cross-appeals from that part of the district
court judgment denying recovery of response costs incurred
before December 11, 1980, and finding appellants and Mills
were not liable for response costs pursuant to § 7003(a) of the
' The Honorable Russell G. Clark, United States District Judge for
the Western District of Missouri.
pay wen
Resource Conservation and Recovery Act of 1976 (RCRA) (also
known as the Solid Waste Disposal Act), as amended, 42
U.S.C.A. § 6973(a) (West Supp. 1986) (appeal No. 84-1853).
For reversal the government argues the district court erred in (1)
finding the government could not recover response costs incur-
red before the effective date of CERCLA, December 11, 1980,
and (2) finding appellants and Mills were not liable for response
costs under RCRA § 7003(a), 42 U.S.C.A. § 6973(a) (West
Supp. 1986).
For the reasons discussed below, we affirm in part, reverse in
part, and remand for further proceedings consistent with this
opinion.
I. FACTS
The following statement of facts is taken in large part from
the district court’s excellent memorandum opinion, United
States v. Northeastern Pharmaceutical & Chemical Co., 579 F.
Supp. 823 (W.D. Mo. 1984) (VEPACCO). NEPACCO was in-
corporated in 1966 under the laws of De'aware; its principal of-
fice was located in Stamford, Connecticut. Although NEPAC-
CO’s corporate charter was forfeited in 1976 for failure to
maintain an agent for service of process, NEPACCO did not
file a certificate of voluntary dissolution with the secretary of
state of Delaware. In 1974 its corporate assets were liquidated,
and the proceeds were used to pay corporate debts and then
distributed to the shareholders. Michaels formed NEPACCO,
was a major shareholder, and was its president. Lee was
NEPACCO’s vice-president, the supervisor of its manufactur-
ing plant located in Verona, Missouri, and also a shareholder.
Mills was employed as shift supervisor at NEPACCO’s Verona
plant.
From April 1970 to January 1972 NEPACCO manufactured
the disinfectant hexachlorophene at its Verona plant. NEPAC-
CO leased the plant from Hoffman-Taff, Inc.; Syntex
Agribusiness, Inc. (Syntex), is the successor to Hoffman-Taff.
— ron
Michaels and Lee knew that NEPACCO’s manufacturing pro-
cess produced various hazardous and toxic byproducts, in-
cluding 2,4,5-trichlorophenol (TCP), 2,3,7,8-tetrachloro-
dibenzo-p-dioxin (TCDD or dioxin), and toluene. The waste
byproducts were pumped into a holding tank which was
periodically emptied by waste haulers. Occasionally, however,
excess waster byproducts were sealed in 55-gallon drums and
then stored at the plant.
In July 1971 Mills approached NEPACCO plant manager Bill
Ray with a proposal to dispose of the waste-filled 55-gallon
drums on a farm owned by James Denney located about seven
miles south of Verona. Ray visited the Denney farm and
discussed the proposal with Lee; Lee approved the use of Mills’
services and the Denney farm as a disposal site. In mid-July
1971 Mills and Gerald Lechner dumped approximately 85 of the
55-gallon drums into a large trench on the Denney farm (Den-
ney farm site) that had been excavated by Leon Vaughn.
Vaughn then fiiled in the trench. Only NEPACCO drums were
disposed of at the Denney farm site.
In October 1979 the Environmental Protection Agency (EPA)
received an anonymous tip that hazardous wastes had been
disposed of at the Denney farm. Subsequent EPA investigation
confirmed that hazardous wastes had in fact been disposed of at
the Denney farm and the site was not geologically suitable for
the disposal of hazardous wastes. Between January and April
1980 the EPA prepared a plan for the cleanup of the Denney
farm site and constructed an access road and a security fence.
During April 1980 the EPA conducted an on-site investigation,
exposed and sampled 13 of the 55-gallon drums, which were
found to be badly deteriorated, and tock water aiid soil
samples. The samples were found to contain ‘‘alarmingly’’ high
concentrations of dioxin, TCP and toluene.
In July 1980 the EPA installed a temporary cap over the
trench to prevent the entry and run-off of surface water and to
minimize contamination of the surrounding soil and ground-
ee
water. The EPA also contracted with Ecology & Environment,
Inc., for the preparation of a feasibility study for the cleanup of
the Denney farm site. Additional on-site testing was conducted.
In August 1980 the government filed its initial complaint against
NEPACCO, the generator of the hazardous substances;
Michaels and Lee, the corporate officers responsible for arrang-
ing for the disposal of the hazardous substances; Mills, the
transporter of the hazardous substances; and Syntex, the owner
and lessor of the Verona plant, seeking injunctive relief and
reimbursement of response costs pursuant to RCRA § 700, 42
U.S.C. § 6973 (count I). In September 1983 the feasibility study
was completed.
In the meantime the EPA had been negotiating with Syntex
about Syntex’s liability for cleanup of the Denney farm site. In
September 1980 the government and Syntex entered into a set-
tlement and consent decree. Pursuant to the terms of the settle-
ment, Syntex would pay $100,000 of the government’s response
costs and handle the removal, storage and permanent disposal
of the hazardous substances from the Denney farm site. The
EPA approved Syntex’s proposed cleanup plan, and in June
1981 Syntex began excavation of the trench. In November 1981
the site was closed. The 55-gallon drums are now stored in a
specially constructed concrete bunker om the Denney farm. The
drums as stored do not present an immineni and substantial ¢ -
dangerment to health or the environment; however, no plan fur
permanent disposal has been developed, and the site will con-
tinue to require testing and monitoring in the future.
In August 1982 the government filed an amended complaint
adding counts for relief pursuant to CERCLA §§ 104, 106, 107,
42 U.S.C. §§ 9604, 9606, 9607 (counts II and III). CERCLA
was enacted afier the filing of the initial complaint. In
September 1982 the district court granted partial summary judg-
ment in favor of the government, holding NEPACCO had the
capacity to be sued under Delaware law. In September 1983 the
district court denied the defense demand for a jury trial, holding
— > wo
the government’s request for recovery of its response costs was
comparable to restitution and thus an equitable remedy. The
trial was conducted during October 1983. The district court fil-
ed its memorandum opinion in January 1984.
Il. DISTRICT COURT DECISION
The district court found that dioxin, hexachlorophene, TCP,
TCB (1,2,3,5-tetrachlorobenzene, also found at the Denney
farm site), and toluene have high levels of toxicity at low-dose
levels and are thus ‘‘hazardous substances’’ within the meaning
of RCRA § 1004(5), 42 U.S.C. § 6903(5), and CERCLA §
101(14), 42 U.S.C. § 9601(14). 579 F. Supp. at 832, 845; see
also United States v. Vertac Chemical Corp., 489 F. Supp. 870,
874-79 (E.D. Ark. 1980) (dioxin). The district court also found
there was a substantial likelihcod that the environment and
human beings would be exposed to the hazardous substances
that had been disposed of at the Denney farm site. 579 F. Supp.
at 846 & n.28 (discussing meaning of ‘‘imminent and substantial
endangerment’’ standard). A state geologist testified the Den-
ney farm site is located in an area in which substances rapidly
move through the soil and into the groundwater and, although
no dioxin had been found in the water in nearby wells, dioxin
had been found as far as 30 inches beneath the soil in the trench.
Id. at 832-33.
A. RCRA Findings
The district court held that RCRA § 7003(a), 42 U.S.C. §
6973(a), requires a finding of negligence in order to hold past
off-site generators and transporters liable for response costs, id.
at 836, and thus RCRA did not apply to past non-negligent off-
site generators and transporters of hazardous substances. /d. at
834-37; accord United States v. A & F Materials Co., 578 F.
Supp. 1249, 1258 (S.D. Ill. 1984); United States v. Waste In-
dustries, Inc., 556 F. Supp. 1301, 1308 (E.D.N.C. 1982), rev’d,
734 F.2d 159 (4th Cir. 1984); United States v. Wade, 546 F.
Supp. 785, 790 (E.D. pa. 1982), appeal dismissed, 713 F.2d 49
yo
(3d Cir. 1983); United States v. Midwest Solvent Recovery, Inc.,
484 F. Supp. 138, 144 (N.D. Ind. 1980).
B. CERCLA Findings
CERCLA § 104, 42 U.S.C. § 9604, authorizes the EPA to
take direct ‘‘response’’ actions, which can include either short-
term ‘‘removal’’ actions or long-term ‘‘remedial’’ actions or
both, pursuant to the NCP, with funds from the ‘‘Superfund,’”?
and to seek recovery of response costs from responsible parties
pursuant to CERCLA § 107, 42 U.S.C. § 9607, in order to
replenish the Superfund. The EPA can also use CERCLA §
106, 42 U.S.C. §9606, to seek injunctions to compel responsible
parties to clean up hazardous waste sites that constitute an ‘‘im-
minent and substantial endangerment”’ to health and the en-
vironment. In the present case, count II sought injunctive relief
pursuant to CERCLA § 106, 42 U.S.C. § 9606, and count III
sought recovery of the government’s past and future response
costs pursuant to CERCLA §§ 104, 107, 42 U.S.C. §§ 9604,
9607.
The district court applied CERCLA retroactively, 579 F.
Supp. at 839, but held the government could not recover
response costs incurred before the effective date of CERCLA,
December 11, 1980. Jd. at 841. The district court also held
CERCLA imposes a standard of strict liability, id. at 843-44,
and that responsible parties can be held jointly and severally
liable, id. at 844-45.
The district court also found NEPACCO liable as an “‘owner
Or operator’ pursuant to CERCLA § 107(a)(1), 42 U.S.C. §
9607(a)(1). Jd. at 847. With respect to the individual defen-
? CERCLA establishes two funds: CERCLA § 232, 42 U.S.C. §
9641, establishes the Post-Closure Liability Trust Fund, which is
funded through taxes on hazardous substances dispose of at
qualified disposal facilities, and the ‘‘Superfund,’’ or Haz rdous
Substances Response Trust, which is funded largely by special taxes
on the petroleum and chemical industries and also by general ap-
propriations.
—
dants, the district court found Mills liable as a ‘‘person who...
accepted any hazardous substances for transport to disposal. . .
sites selected by such person,’’ pursuant to CERCLA §
107(a)(4), 42 U.S.C. § 9607(a)(4). Id. Mills was not represented
by counsel in the district court and has not appealed. The
district court also found Lee liable as an ‘‘owner or operator’’
pursuant to CERCLA § 107(a)(1), 42 U.S.C. § 9607(a)(1), and
as a ‘‘person who by contract, agreement, or otherwise. . . ar-
ranged with a transporter for transport for disposal . . . of
hazardous substances,’’ pursuant to CERCLA § 107(a)(3), 42
U.S.C. § 9607(a)(3). Id. at 847-49. The district court found
Michaels liable as a person who arranged for the transport and
disposal of hazardous substances pursuant to CERCLA §
107(a)(3), 42 U.S.C. § 9607(a)(3). Jd. at 849 n.31. The liability
of NEPACCO, Lee, Michaels, and Mills was joint and several.
Id. at 849-50.
The district court further found the government’s right to
recovery of response costs was very broad and included litiga-
tion costs, attorney’s fees, future response costs, and prejudg-
ment interest, and that the defendants in an action by the
government for recovery of response costs had the burden of
proving that the government’s response costs were inconsistent
with the NCP. /d. at 850-52. NEPACCO, Michaels and Lee
have appealed. Mills has not appealed. The government filed a
cross-appeal. Syntex filed an amicus curiae brief, generally in
support of appellants’ retroactivity arguments.’
> We do not consider in this appeal and cross-appeal the arguments
raised by Syntex about causation, strict liability, joint and several
liability, and separation of powers. Syntex, as amicus, cannot raise
issues not raised by the parties. See, e.g., preservation Coalition, Inc.
v. Pierce, 667 F.2d 851, 861-62 (9th Cir. 1982); Bing v. Roadway Ex-
press, Inc., 485 F.2d 441, 452 (Sth Cir. 1973). Most cases have impos-
ed strict liability and joint and several liability under RCRA and
CERCLA. See, e.g., United States v. Ottati & Goss, Inc., 630 F.
Supp. 1361, 1395-96, 1401 (D.N.H. 1985); United States v. Conserva-
tion Chemical Co., 619 F. Supp. 162, 191, 198-99, 204 (W.D. Mo.
1985); United States v. Chem-Dyne Corp., 572 F. Supp. 802, 808-11
(S.D. Ohio 1983). See also Developments in the Law— Toxic Waste
Litigation, 99 Harv. L. Rev. 1498, 1517-43 (1986).
ee ee eT
— > va
lil. CERCLA— RETROACTIVITY
A. Application of CERCLA to Pre-1980 Acts.
Appellants first argue the district court erred in applying
CERCLA retroactively, that is, to impose liability for acts com-
mitted before its effective date, December 11, 1980. CERCLA §
302(a), 42 U.S.C. § 9652(a), provides that ‘‘[u]nless otherwise
provided, all provisions of this chapter shall be effective on
December 11, 1980.’’ Appellants argue that CERCLA should
not apply to pre-enactment conduct that was neither negligent
nor unlawful when committed. Appeliants argue that all the
conduct at issue occurred in the early 1970s, well before
CERCLA became effective. Appellants also argue that there is
no language supporting retroactive application in CERCLA’s
liability section, CERCLA § 107, 42 U.S.C. § 9607, or in the
legislative history. Appellants further argue that because
CERCLA imposes a new kind of liability, retroactive applica-
tion of CERCLA violates due process and the taking clause. We
disagree.
The district court correctly found Congress intended
CERCLA to apply retroactively. Jd. at 839. We acknowledge
there is a presumption against the retroactive application of
statutes. See United States v. Security Industrial Bank, 459
U.S. 70, 79 (1982). We hold, however, that CERCLA § 302(a),
42 U.S.C. § 9652(a), is ‘‘merely a standard ‘effective date’ pro-
vision that indicates the date wnen an action can first be
brought and when the time begins to run for issuing regulations
and doing other future acts mandated by the statute.’’ United
States v. Shell Oil Co., 605 F. Supp. 1064, 1075 (D. Colo. 1985);
cf. Von Allmen v. Connecticut Teachers Retirement Board, 613
F.2d 356, 359-60 (2d Cir. 1979) (veterans statute).
Although CERCLA does not expressly provide for retroac-
tivity, it is manifestly clear that Congress intended CERCLA to
have retroactive effect. The language used in the key liability
provision, CERCLA § 107, 42 U.S.C. § 9607, refers to actions
eet |
— A-10 —
and conditions in the past tense: ‘‘any person who at the time of
disposal of any hazardous substances owned or operated,”’
CERCLA § 107(a)(2), 42 U.S.C. § 9607(a)(2), ‘‘any person who
. arranged with a transporter for transport for disposal,’’
CERCLA § 107(a)(3), 42 U.S.C. § 9607(a)(3), and ‘‘any person
who .. . accepted any hazardous substances for transport to...
sites selected by such person,’’ CERCLA § 107(a)(4), 42 U.S.C.
§ 9607(a)(4). See, e.g., United States v. Conservation Chemical
Co., 619 F. Supp. 162, 220 (W.D. Mo. 1985); United States v.
Sheli Oil Co., 605 F. Supp. at 1069-73; United States v. South
Carolina Recycling & Disposal, Inc., 20 EnvRt Rep. Cases
(BNA) 1753, 1760-62 (D.S.C. 1984)‘; United States v. A & F
Materials Co., 577 F. Supp. at 1259; United States v. Price, 577
F. Supp. 1103, 1111-12 (D.N.J. 1983); Ohio ex rel. Brown v.
Georgeoff, 562 F. Supp. 1300, 1312 (N.D. Ohio 1983); United
States v. Outboard Marine Corp., 556 F. Supp. 54, 57 (N.D. Il.
1982); United States v. Reilly Tar & Chemical Corp., 546 F.
Supp. 1100, 1113-14 (D. Minn. 1982); see generally
Developments in the Law— Toxic Waste Litigation, 99 Harv.
L. Rev. 1498 (1986) (Developments).
Further, the statutory scheme itself is overwhelmingly
remedial and retroactive. CERCLA authorizes the EPA to
force responsible parties to clean up inactive or abandoned
hazardous substance sites, CERCLA § 106, 42 U.S.C. § 9606,
and authorizes federal, state and local governements and private
parties to clean up such sites and then seek recovery of their
response costs from responsible parties, CERCLA §§ 104, 107,
42 U.S.C. §§ 9604, 9607. In order to be effective, CERCLA
‘ The court in United States v. South Carolina Recycling &
Disposal, Inc., 20 Env’t Rep. Cases (BNA) 1753, 1760 (D.S.C. 1984),
noted CERCLA does not appiy ‘‘retroactively’’ because it does not
impose liability for past conduct; rather, CERCLA imposes liability
upon those parties responsibie for causing certain conditions, that is,
the release or threatened release or hazardous substances, that are the
present or future results of their past actions.
— A-ll —
must reach past conduct. CERCLA’s backward-looking focus
is confirmed by the legislative history. See generally H.R. Rep.
No. 1016, 96th Cong., 2d Sess., reprinted ir 1980 U.S. Code
Cong. & Ad. News 6119 (CERCLA House Report). Congress
intended CERCLA ‘“‘to initiate and establish a comprehensive
response and financing mechanism to abate and control the vast
problems associated with abandoned and inactive hazardous
waste disposal sites.’’ Jd. at 22, 1980 U.S. Code Cong. & Ad.
News at 6125.
The district court also correctly found that retroactive ap-
plication of CERCLA does not violate due process. 579 F.
Supp. at 840-41. Appellants argue CERCLA creates a new
form of liability that is designed to deter and punish those who,
according to current standards, improperly disposed of hazar-
dous substances in the past. We disagree.
It is by now well established that legislative Acts ad-
justing the burdens and benefits of economic life come to
the Court with a presumption of constitutionality, and that
the burden is on one complaining of a due process viola-
tion to establish that the legislature has acted in an ar-
bitrary and irrational way. [L]egislation readjusting rights
and burdens is not unlawful solely because it upsets other-
wise settled expectations. This is true even though the ef-
fect of the legislation is to impose a new duty or liability
based on past acts.
Usery v. Turner Elkhorn Mining Co., 428 U.S. 1, i5 (1976)
(citations omitted). Due process is satisfied ‘‘simply by showing
tht the retroactive application of the legislation is itself justified
by a rational legislative purpose.’’ Pension Benefit Guarunty
Corp. v. R.A. Gray & Co., 467 U.S. 717, 730 (1984). ‘‘Provid-
ed that the retroactive application of a statute is supported by a
legitimate legislative purpose furthered by rational means,
judgments about the wisdom of such legislation remain within
the exclusive province of the legislative and executive branches .
ee © wr.
— A-12 —
Appellants failed to show that Congress acted in an arbitrary
and irrational manner. Cleaning up inactive and abandoned
hazardous waste disposal sites is a legitimate legislative purpose,
and Congress acted in a rational manner in imposing liability
for the cost of cleaning up such sites upon those parties who
created and profited from the sites and upon the chemical in-
dustry as a whole, NEPACCO, 579 F. Supp. at 841. See United
States v. Ottati & Goss, Inc., 630 F. Supp. 1361, 1398-99
(D.N.H. 1985); United States v. Conservation Chemical Co.,
619 F. Supp. at 221-22; United States v. Shell Oil Co., 605 F.
Supp. at 1072-73; United States v. South Carolina Recycling &
Disposal, Inc., 20 Env’t Rep. Cases (BNA) at 1761-62; see
generally Developments, 99 Harv. L. Rev. at 1556-62. We hold
retroactive application of CERCLA to impose liability upon
responsible parties for acts committed before the effective date
of the statute does not violate due process.
Appellants also summarily argue retroactive application of
CERCLA constitutes an unconstitutional taking of property.
We disagree. First, because appellants do not have a property
interest in the Denney farm site, we question appellants’ stan-
ding to raise a taking issue. Second, we hesitate to characterize
the government’s cleanup as a taking at all; the government’s
cleanup of the Denney farm site has not deprived the property
owner of any property interest. See United States v. Conserva-
tion Chemical Co., 619 F. Supp. at 216-17. Instead, the govern-
ment’s cleanup of the site abated an ‘‘imminent and substantial
endangerment’’ to the public health and the environment, thus
eliminating a public nuisance and restoring value to the property
by removing the hazardous substances. See generally
Developments, 99 Harv. L. REv. at 1564-65 & nn.111, 114,
citing Blaymore, Retroactive Application of Superfund: Can
Oid Dogs Be Taught New Tricks?, 12 B.C. Envtl. Aff. L. Rev.
1, 43-46 (1985).
— A-13 —
B. Application of CERCLA to Pre-1980 Costs
Related to the question of CERCLA’s application to pre-1980
acts is the question whether the government can recover
response costs incurred prior to CERCLA’s effective date. This
issue is raised by the government’s cross-appeal. The district
court held that the government could not recover its pre-
enactment response costs. NEPACCO, 579 F. Supp. at 841-43.
The government argues on cross-appeal that the district court
erred in denying the government recovery of its pre-eCERCLA
response costs. The government argues a close examination of
the statutory language and scheme, legislative history and
legislative purpose supports retroactive liability for pre-
enactment response costs.
The district court concluded that because of the magnitude of
the potential liability for pre-enactment response costs, ‘‘it is
difficult to believe that if Congress had intended to make the
defendants liable for pre-CERCLA expenses, it would not have
said so explicitly and clearly in the statutory language, commit-
tee reports or floor debates.’’ Id. at 843; accord United States
v. Wade, 20 Env’t Rep. Cases (BNA) 1849, 1850-51 (E.D. Pa.
1984). The district court found that CERCLA itself did not
clearly specify whether pre-enactment response costs were
recoverable because the ‘‘statutory language ‘all costs . . . incur-
red’ [in CERCLA § 107(a),] 42 U.S.C. § 9607(a), is susceptivle
to varying interpretations, either all costs incurred regardless of
when incurred or all costs incurred from the date of
enactment.’’ Jd. at 842. The district court noted that ‘‘[t]he
[NCP] makes no provision for the recovery of pre-CERCLA
response costs,”’ id., citing 40 C.F.R. Part 300 (1983), and that
the ‘‘time limitations placed in sections 104(c)(3), 107(f) and
111(d)(1) [,42 U.S.C. §§ 9607(c)(3), (f), 9677(d),}] could equally
indicate that these are the only provisions in which pre-
CERCLA costs may be recoverable.’’ Id. The district court also
found the legislative history ‘‘unpersuasive’’ because recovery
of pre-CERCLA response costs was not discussed at all in the
— on
House, id. at 843 n.21, and the only references to authority to
recover pre-CERCLA response costs in the Senate, § 4(a))2) and
§ 4(n) of S. 1480, were deleted and not enacted. /d. at 843.
After the present case was decided, this issue was exhaustively
examined and resolved in favor of recovery of pre-CERCLA
response costs in United States v. Shell Oil Co., 605 F. Supp. at
1072-79. We find the analysis in United States v. Shell Oil Co.
to be convincing. Accord Mayor of Boonton v. Drew Chemical
Corp., 621 F. Supp. 663, 668-69 (D.N.J. 1985); United States v.
Ward, 618 F. Supp. 884, 989-99 (E.D.N.C. 1985).
In United States v. Shell Oil Co. the federal government sued
under CERCLA §§ 104, 107, 42 U.S.C. §§ 9604, 9607, to
recover the costs it had incurred and will incur in cleaning up the
heavily contaminated Rocky Mountain Arsenal located outside
of Denver, Colorado. The Rocky Mountain Arsenal has been
owned by the United States since 1942 and was used by the
United States Department of the Army for manufacturing and
handling various chemicals and munitions. In addition, since
1947, Shell Oil and its predecessors had leased part of the
Arsenal for the manufacture of pesticides, herbicides and other
chemicals. The Army’s wastes and all or some of Shell’s wastes
were disposed of through, waste disposal systems built and
operated by the Army. The waste disposal systems repeatedly
failed and released the commingled wastes into the environ-
ment, severely contaminating the Arsenal and threatening the
surrounding environment. In 1975 the Army began to clean up
the Arsenal. By December 1, 1983, before CERCLA was
enacted, the Army had incurred about $48 million in response
costs and, by January 1984, had proposed four alternative
cleanup programs, with estimated future response costs ranging
from $210 million to $1.8 billion, and recommended the pro-
gram estimated to cost $360 million. Shell argued, among other
things, that CERCLA did not authorize recovery of the Army’s
pre-enactment response costs.
— A-15 —
The Shell Oil court disagreed and held CERCLA authorized
recovery of pre-enactment response costs. 605 F. Supp. at 1079.
First, the Shel/ Oil court agreed with the district court in the pre-
sent case-that ‘‘congressional intent to either impose or
withhold liability for response costs incurred before CERCLA
cannot be divined from the verb tenses in [CERCLA] § 107)a)
[,.42 U.S.C. § 9607(a)].’’ Jd. at 1073. The Shell Oii court ex-
amined the grammatical structure of CERCLA § 107(a), 42
U.S.C. § 9607(a), and concluded hat each party’s argument
cancelled the other out. J/d., cit 1g Ohio ex rel. Brown v.
Georgeoff, 562 F. Supp. at 1309-10. Shell had argued that ‘‘use
of the imperative ‘shall’ . . . indicate[d] [that Congress] intend-
ed prospective operation of the liability provision.’’ 605 F.
Supp. at 1073. The government had argued, however, that ‘‘all
the other verbs in [CERCLA] § 107(a) [, 42 U.S.C. § 9607(a),]
including ‘costs . . . incurred,’ [were] in the past tense (with the
exception of ‘accepts’). . . . [and thus should] be interpreted to
include pre-enactment events.’’ Jd.
The Shell Oil court did not address the NCP’s failure to pro-
vide for recovery of pre-CERCLA response costs. The Shell Oil
court, however, considered and rejected the related argument
that the requirement in CERCLA § 107(a), 42 U.S.C. § 9607(a),
that recoverable costs were those costs ‘‘not inconsistent with
the [NCP]’’ indicated Congress’ intent that liability for costs
was prospective only. The She// Oil court concluded the ‘‘[t}he
consistency requirement addresses the nature of the response ac-
tion for which costs can be recovered, not the timing of the ac-
tion.’’ Jd. at 1074. The Sheil/ Oil court also refused to interpret
the effective date provision, CERCLA § 302(a), 42 U.S.C. §
9652(a), to limit liability to pre-enactment response costs. /d. at
1075.
Because CERCLA §§ 107(c)(3), 107(f) and 111(d), 42 U.S.C.
§§ 9607(c)(3), (f), 9611(d), contain express time limitations, the
absence of any time limitations in CERCLA § 107(a), 42 U.S.C.
§ 9607(a), arguably supports only prospective liability for
— A-16 —
response costs. CERCLA § 107(c)(3), 42 U.S.C. § 9607(c)(3),
provides a state with a credit against its share of future
maintenance costs for its documented cleanup costs expended
after January 1, 1978 and before December 11, 1980, for
CERCLA § 111, 42 U.S.C. § 9611, actions. This provision
specifies the funding relationship between the federal govern-
ment and individual states for future maintenance costs and
does not address whether the government can recover pre-
CERCLA response from responsible parties.
CERCLA § 107(a)(4)(A)-(C), 42 U.S.C. § 9607(a)(4)(A)-(C),
sets forth three types of liability: (A) response costs incurred by
the United States or a state that are not inconsistent with the
NCP, (B) any other necessary response costs incurred by any
other person that are consistent with the NCP, and (C) natural
resource damages. By separately considering the place of each
type of liability in the statutory scheme, we can discern Congres-
sional intent with respect to recovery of pre-enactment response
costs. CERCLA §§ 107(f), 111(d)(1), 42 U.S.C. §§ 9607(f),
9611(d)(1), preclude recovery of natural resource damages and
claims for such damages against the Superfund if the release of
hazardous substances and the resulting natural resource injury
occurred wholly before CERCLA’s enactment. The Sheil Oil
court noted the provisions authorizing recovery of response
costs by the government, CERCLA § 107(a)(4)(A), 42 U.S.C. §
9607(a)(4)(A), and by any other person, CERCLA §
107(a)(4)(B), 42 U.S.C. § 9607(a)(4)(B), do not contain time
limitations and decided ‘‘[iJn order to give meaning to these
[time limitation] provisions [in CERCLA §§ 107(f), 111(d)(1),
42 U.S.C. §§ 9607(f), 9611(d)(1)], one must assume that liability
for other damages — costs of removal or remedial action incur-
red by the United States or a State (§ 107(a)(4)(A)), and other
necessary response costs incurred by any other person (§
107(a)(4)(B)) — is not so limited.’’ 605 F.Supp. at 1076. Thus,
the Shell Oil court concluded ‘‘Congress implicitly authorized
retroactive application of sections 107(a)(4)(A) and (B) by affir-
matively limiting retroactive application of the third category of
—
liability, damages to natural resources, section 107(a)(4)(C).”’
Id. Cf. United States v. Conservation Chemical Co. 619 F.
Supp. at 213 (three year statute of limitations in CERCLA §
112(d), 42 U.S.C. § 9612(d), applies only to claims against the
Superfund and for natural resource damages), citing United
States v. Mottolo, 605 F. Supp. 898, 901-10 (D.N.H. 1985).
As further explained by the She// Oil court
[t]here is good reason to preclude use of CERCLA
monies and liability for cleanup of sites where both the
release and the damages occurred wholly before enact-
ment. The sites excluded under 107(f) and 111(d) are
stable sites, that is, the environment, though damaged, will
not deteriorate further. ...Congress apparently decided to
utilize the limited resources of the fund created by
CERCLA to clean up the thousands of sites. . .which are
not stable. CERCLA’s goal is to clean up these sites
before further damage occurs.
At the opposite end of the spectrum from the stable sites
excluded under 107(f) and 111(d) are those sites. . .where
the danger to the public health and welfare and to the en-
vironment was so imminent that the United States proceed-
ed with cleanup without a special fund of money for that
purpose and without assurance that it would be repaid by
the persons responsible for the contamination. It was sites
containing this magnitude of public danger that prompted
Congress to enact CERCLA.
Construing section 107(a) to preclude recovery of pre-
enactment response costs would carve out an exception to
the general retroactive scheme of the statute for those most
severe situations where. . .the government’s response com-
menced prior to the enactment of the statute. ... Congress
could [not] have intended to protect the public fisc by im-
posing liability on the responsible parties, yet except the
sites where response had already commenced because the
'
— A-18 —
situations were the most imminently threatening. Such an
interpretation would penalize the government for prompt
response and provide an undeserved windfall to the parties
who had created, then abandoned, some of the most
egregious sites.
605 F. Supp. at 1076-77.
The Shell Oil court then reviewed the legislative history of
CERCLA, including the treatment of § 4(a)(2) and § 4(n) of S.
1480, and concluded it supported imposing liability for pre-
enactment response costs. Jd. at 1077-79. The legislative
history of CERCLA is very difficult to follow, in part because
[t]wo different bills proceeded through the House and the
Senate. The Senate made certain last minute amendments
to its bill, (S. 1480, 96th Cong., 2d Sess. 1980), most
notably the removal of provisions imposing liability for
personal injury caused by hazardous waste disposal. The
House then struck the language in its bill, H.R. 7020, 96
Cong.2d Sess. (1980), and substituted the language of the
Senate bill. H.R. 7020, as amended, was eventually
enacted. The bill retained the House file number, ap-
parently because of a requirement that appropriations
measures Originate in the House.
United States v. Reilly Tar & Chemical Corp., 546 F. Supp. at
1111. As explained by the Shel! Oil court
[t}he liability provisions of CERCLA were derived large-
ly from the original Senate bill, S. 1480. S. 1480 contained
a liability provision for both costs of removal (§ 4(a)(1))
and for natural resources, property and personal injury
damages (§ 4(a)(2)). During discussions of S. 1480 in the
Senate Committee on Environment and Public Works,
concern was expressed about retroactive application of the
bill. ... Senator Domenici introduced a new § 4(n) which
limited recovery for pre-enactment damages recoverable
under § 4(a)(2).
— A-19 —
Significantly, § 4(n)(1) did not apply to § 4(a)(1) which
provided liability for response costs. The Senate report [at
37] emphasized the limited scope of § 4(n): .. .‘*Costs of
removal (cleanup and containment) are not affected by this
provision, nor are any damages associated with continuing
releases.”’
605 F. Supp. at 1077-78. As noted by the district court in the
present case, both § 4(a)(2) and § 4(n) were deleted from the
enacted bill. 579 F. Supp. at 843. We agree with the Shei/ Oil
court, however, that the deletion of these subsections in fact in-
dicates Congress intended to permit recovery of pre-CERCLA
response costs because
[t]he time limitations on damages added by § 4({n) of S.
1840 were maintained in the final version of CERCLA as
the §§ 107(f) and 111(d) limitations on recovery of natural
resources damages. The remaining time limitations of §
4(n) were deleted only because the substantive liability pro-
visions for property and personal injury damages [in §
4(a)(2)] were deleted from the statute. Thus, the scheme of
§ 4(n) in limiting recovery for pre-enactment damages, but
not response costs, was maintained in the final statute. The
legislative history of § 4(n), including the comments em-
phasizing that recovery of removal costs is not to be
limited by retroactivity concerns, therefore applies to the
statute as passed.
605 F. Supp. at 1079 (emphasis added).
In summary, we hold the district court erred in finding that
CERCLA does not authorize recovery of pre-enactment
response costs. That part of the district court judgment holding
that pre-enactment response costs cannot be recovered is revers-
ed.
—
IV. RCRA
A. Standard and Scope of § 7003 Liability
As an alternative basis for recovery of the response costs in-
curred before December 11, 1980, the government argues on
cross-appeal that it can also recover its response costs pursuant
to RCRA § 7003(a), 42 U.S.C.A. § 9673(a) (West Supp. 1986).
The district court did not reach the recovery issue because it
held that under RCRA § 7003(a), 42 U.S.C. § 6973(a) (prior to
1984 amendments discussed below), proof of fault or negligence
was required in order to impose liability upon past off-site
generators and transporters. 579 F. Supp. at 834-37. Because
the government did not allege or prove negligence, the district
court found no liability under RCRA § 7003(a), 42 U.S.C. §
9673(a) (prior to 1984 amendments). /d. at 837. The govern-
ment argues that the standard of liability under RCRA §
7003(a), 42 U.S.C.A. § 6973(a) (West Supp. 1986), as initially
enacted and as amended in 1984, is strict liability, not
negligence, and that liability under RCRA can be imposed even
though the acts of disposal occurred before RCRA became ef-
fective in 1976. We agree.
RCRA was initially enacted in 1976, Pub. L. No. 94-580, 90
Stat. 2826 (1976), and was amended in 1978, Pub. L. No.
95-609, 92 Stat. 3083 (1978), and 1980, Pub. L. No. 96-482, 92
Stat. 2348 (1980). In November 1984, after the district court’s
January 1984 decision in the present case, RCRA was again
amended by the Hazardous and Solid Waste Amendments of
1984, Pub. L. No. 98-616, 98 Stat. 3271 (1984) (1984 amend-
ments). We have considered the 1984 amendments and the ac-
companying legislative history and, for the reasons discussed
below, we believe the 1984 amendments support the govern-
ment’s arguments about RCRA’s standard and scope of liability
and retroactivity.
The critical issue is the meaning of the phrase ‘‘contributing
to.’’ Before its amendment in 1984, RCRA § 7003(a), 42
— A-21 —
U.S.C. § 6973(a), imposed liability upon any person ‘“‘con-
tributing to’’ ‘‘the handling, storage, treatment, transportation
or disposal of any solid or hazardous waste’’ that ‘‘may present
an imminent and substantial endangerment to health or the en-
vironment.’’ The district court did not find either the statutory
language or the statutory framework helpful in determining
whether past non-negligent off-site generators and transporters
were liable under RCRA § 7003(a), 42 U.S.C. § 6973(a) (prior to
the 1984 amendments). 579 F. Supp. at 834. The district court
then considered the legislative history of the 1980 amendments,
id. at 835-36, because ‘‘[t]he legislative history of the [RCRA] as
originally enacted contains no specific discussion of the reach of
section 7003 and no mention of the reasons for its insertion. The
hastiness of the [RCRA’s] passage in the final days of a congres-
sional session has been well-documented.’’ United States v.
Waste Industries, Inc. 734 F.2d 159, 165 (4th Cir. 1984), citing
Kovacs & Klucsik, The New Federal Role in Solid Waste
Managemet: The Resource Conservation & Recovery Act of
1976, 3 Colum. J. Envtl. L. 205, 216-20 (1976).
The district court found two apparently contradictory
references in the legislative history. The report on Hazardous
Waste Disposal issued by the Subcommittee on Oversight and
Investigations of the Committee on Interstate aad Foreign
Commerce, H.R. Comm. Print No. IFC 31, 96th Cong., Ist
Sess. 31 (1979) (the Eckhardt Report), stated that ‘‘a company
that generates hazardous waste would be someone ‘contributing
to’ an endangerment under § 7003, even where someone else
deposited the waste in an improper disposal site similar to strict
liability under common law.”’ The strict liability language in the
Eckhardt Report, however, was not adopted later in the Senate
Report, which stated
a company that generated hazardous waste might be so-
meone ‘‘contributing to’’ air endangerment under section
7003 even where someone else deposited the waste in an
improper disposal site (similar to strict liability under com-
mon law), where the generator had knowledge of the illicit
—
disposal or failed to exercise due care in selecting or in-
structing the entity actually conducting the disposal.
S. Rep. No. 172, 96th Cong., 2d Sess. 5, reprinted in 1980 U.S.
Code Cong. & Ad. News 5019, 5023. The district court resolved
the battle between the conflicting legislative references in favor
of the Senate Report and held that the language in the Senate
Report ‘‘would suggest strict liability of present responsible lan-
downers, but the qualifying phrases ‘illicit disposal or failed to
exercise due care’ requires a finding of negligence prior to
holding past off-site generators or transporters liable.’’ 579 F.
Supp. at 836; accord United States v. Waste Industries, Inc.,
556 F. Supp. at 1308; United States v. Wade, 546 F. Supp. at
790. But see, e.g., United States v. Reilly Tar & Chemical Corp.
546 F. Supp. at 1108; United States v. Price, 523 F. Supp. 1055,
1070-71 (D.N.J. 1981), aff’d, 688 F.2d 204 (3d Cir. 1982);
United States v. Diamond Shamrock Corp., 17 Env’t Rep.
Cases (BNA) 1329, 1333-34 (N.D. Ohio 1981); United States v.
Solvents Recovery Service, 496 F. Supp. 1127, 1139 (D. Conn.
1980).
Then, in November 1984, Congress passed and President
Reagan signed the 1984 amendments, which were described as
‘*clarifying’’ amendments and specifically addressed the stan-
dard and scope of liability of § 7003(a). As amended in 1984,
RCRA § 7003(a), 42 U.S.C.A. § 6973(a) (West Supp. 1986)
(new language underlined; deleted language in brackets), now
provides in pertinent part:
Notwithstanding any other provision of this chapter, upon
receipt of evidence that the past or present handling,
storage, treatment, transportation or disposal of any solid
waste or hazardous waste may present an imminent and
substantial endangerment to health or the environment,
the Administrator may bring suit on behalf of the United
States in the appropriate district court [to immediately
restrain any person] against any person (including any past
or present generator, past or present transporter, or past or
— A-23 —
present owner or operator of a treatment, storage, or
disposal facility) who has contributed or who is con-
tributing to such handling, storage, treatment, transporta-
tion or disposal [to stop] to reatrain such person from such
handling, storage, treatment, transportation, or disposal
[or to take such other action as may be necessary], /o order
such person to take such other action as may be necessary,
or both.
As amended, RCRA § 7003(a), 42 U.S.C.A. § 6973(a) (West
Supp. 1986), specifically applies to past generators and
transporters. See United States v. Ottari & Gross, Inc. 630 F.
Supp. at 1400 (applying RCRA as amended in 1984); United
States v. Conservation Chemical Co., 619 F. Supp. at 217-18
(applying RCRA as amended in 1984).
Congress’ intent with respect to the standard of liability under
RCRA § 7003(a), 42 U.S.C.A. § 6973(a) (West Supp. 1986), as
amended by the 1984 amendments, is clearly set forth in the ac-
companying House Conference Report.* The House Con-
* The earlier House Report also stated:
[t]hese amendments are intended to clarify the breadth of Sec-
tion 7003 as to the persons, conditions and acts it covers. The
amendments clearly provide that anyone who has contributed or
is contributing to the creation, existence, or maintenance of an
imminent and substantial endangerment is subject to the
equitable authority of Section 7003, without regard to fault or
negligence. Such persons include, but are not limited to, past
and present generators (both off-site and on-site) of hazardous
wastes, past and present owners and operators of waste treat-
ment, storage, or disposal facilities, and past and present
transporters of solid or hazardous wastes. \n addition, Section
7003 is clarified to establish that it applies to any act, whether
past or present, which has resulted in or may result in an immi-
nent and substantial endangerment to public health or the en-
vironment....
As evidenced by the definition of ‘‘disposal’’ in Section
1004(3), which includes the ‘‘leaking’’ of hazardous wastes, Sec-
tion 7003 has always provided the authority to require the abate-
ie il ill
——
ference Report also expressly disapproved of the Wade and
Waste Industries cases, which were relied upon by the
NEPACCO court, as well as the NEPACCO decision itself. The
House Conference Report stated:
ment of present conditions of endangerment resulting from past
disposal practices, whether intentional or unintentional... .
Moreover, because Section 7003 focuses on the abatemeni of
conditions threatening health and the environment and not a
particular human activity, it has a/ways reached those persons
who have contributed in the past or are presently contributing to
the endangerment, including but not limited to generators,
regardless of fault or negligence. The amendment, by adding
the words ‘‘have contributed”’ is merely intended to clarify the
existing authority. Thus, for example, non-negligent generators
whose wastes are no longer being deposited or dumped at a par-
ticular site may be ordered to abate the hazard to health or the
environment posed by the leaking of wastes they once deposited
or caused to be deposited on the site. The amendment reflects
the long-standing view that generators and other persons involv-
ed in the handling, storage, treatment, transportation, or
disposal of hazardous wastes must share in the responsibility for
the abatement of the hazards arising from their activities.
In addition, due to the nature of the hazards presented by
disposal sites , Section 7003 is ‘‘intended to confer upon the
courts the authority to grant affirmative equitable relief to the
extent necessary to eliminate any risks posed by toxic wastes.”’
United States v. Price, 688 F.2d 204, 213-14 (3d Cir. 1982). The
section was intended and is intended to abate conditions
resulting from past activities. Hence, the lower court decisions
in United States v. Wade, 546 F. Supp. 785 (E.D. Pa. 1982), and
United States v. Waste Industries, Inc., No. 80-4-Civ-7
(E.D.N.C. 1983), which restricted the application of Section
7003, are inconsistent with the authority conferred by the section
as initially enacted and with these clarifying amendments.
H.R. Rep. No. 198 (Part I), 98th Cong., 2d Sess. 47-49 (1983) (em-
phasis added), reprinted in 1984 U.S. Code Cong. & Ad. News 5576,
5606-09 (emphasis added).
— A-25 —
Section 7003 focuses on the abatement of conditions
threatening health and the environment and not particular-
ly human activity. Therefore, it has always reached those
persons who have contributed in the past or are presently
contributing to the endangerment, including but not
limited to generators, regardless of fault or negligence. The
amendment, by adding the words ‘‘have contributed’’ is
merely intended to clarify the existing authority. Thus, for
example, non-negligent generators whose wastes are no
longer being deposited or dumped at a particular site may
be ordered to abate the hazard to health or the environ-
ment posed by the leaking of the wastes they once
generated and which have been deposited on the site. The
amendment reflects the long-standing view that generators
and other persons involved in the handling, storage, treat-
ment, transportation or disposal of hazardous wastes must
share in the responsibility for the abatement of the hazards
arising from their activities. The section was intended and
is intended to abate conditions resulting from past ac-
tivities. Hence, the district court decisions in United States
v. Wade, 546 F. Supp. 785 (E.D. Pa. 1982), United States
v. Waste Industries, Inc., No. 80-4-Civ-7 (E.D.N.C. 1983),
and United States v. Northeastern Pharmaceutical &
Chemical Co., 579 F. Supp. 823 (W.D. Mo. 1984), which
restricted the application of section 7003, are inconsistent
with the authority conferred by the section as initially
enacted and with these clarifying amendments.
H.R. Conf. Rep. No. 1133, 98th Cong., 2d Sess. 119 (1984)
(emphasis added), reprinted in 1984 U.S. Code Cong. & Ad.
News 5649, 5690 (emphasis added).
Thus, following the 1984 amendments, past off-site
generators and transporters are within the scope of RCRA §
7003(a), 42 U.S.C.A. § 6973(a) (West Supp. 1986). From the
legislative history of the 1984 amendments, it is clear that Con-
gress intended RCRA § 7003(a), 42 U.S.C.A. § 6973(a) (West
— A-26 —
Supp. 1986), as initially enacted and as amended, to impose
liability without fault or negligence and to apply to the present
conditions resulting from past activities. In other words, RCRA
§ 7003(a), 42 U.S.C.A. § 6973(aj (West Supp. 1986), as initially
enacted and as amended, applies to past non-negligent off-site
generators like NEPACCO and to non-negligent past
transporters like Mills. See United States v. Ottati & Goss, Inc.,
630 F. Supp. at 1400-01 (applying RCRA as amended in 1984),
citing United States v. Hardage, 18 Env’t Rep. Cases (BNA)
1685, 1686 (W.D. Okla. 1982) (RCRA as amended in 1980);
United States v. Conservation Chemical Co., 619 F. Supp. at
198.
Appellants argue, however, that the 1984 amendments should
not be applied to them because the 1984 amendments are not
merely ‘‘clarifying’’ amendments but instead substantively
changed the existing law. We disagree. First, Congress itself ex-
pressly characterized the 1984 amendments as ‘‘clarifying’’
amendments. Second, as part of the legislative history of the
1984 amendments, Congress expressly stated what its intention
had been when it initially passed the RCRA in 1976, even
though the 1976 legislative history contained no specific discus-
sion of the standard and scope of liability of § 7003(a).
Although this is not legislative history as such, the views of
subsequent Congresses on the same or similar statutes are
entitled to some weight in the construction of previous
legislation. Although the views of subsequent Congresses
cannot override the unmistakable intent of the enacting
one, this is not a problem in this case because there was no
absolutely ‘‘unmistakable intent’’ of Congress concerning
section 7003. To the extent that the precise intent of the
enacting Congress may be obscure, the views of subse-
quent Congresses should be given greater deference than
they wouid be otherwise entitled to receive.
United States v. Waste Industries, Inc., 734 F.2d at 166 (discuss-
ing legislative history of 1980 RCRA amendments) (citations
—
omitted); see also Seatrain Shipbuilding Corp. v. Shell Oil Co.,
444 U.S. 572, 596 (1980). Thus, by passing the 1984 amend-
ments, the 98th Congress made clear that the intention of the
94th Congress in enacting the RCRA in 1976 had been to impose
liability upon past non-negligent off-site generators and
transporters of hazardous waste.
B. Retroactivity
This argument is closely related to the question of the scope
of § 7003(a) liability discussed above. Appellants argue that
because RCRA, unlike CERCLA, is prospective in focus and
was not enacted until 1976, RCRA cannot be retroactively ap-
plied to impose liability on them for acts that occurred in 1971.
A similar retroactivity argument was raised in United States v.
Price, 523 F. Supp. at 1071-72. The defendants in United States
v. Price had argued that RCRA could not be applied retroac-
tively to impose liability on them for disposing of toxic wastes in
1972. The Price court rejected the retroactivity argument,
stating
[t]he gravamen of a section 7003 action . . . is not defen-
dants’ dumping practices, which admittedly ceased with
respect to toxic wastes in 1972, but the present imminent
hazard posed by the continuing disposal [, which is defined
by RCRA § 1003(3), 42 U.S.C. § 6903(3), to include *‘[t}he
... leaking... of any solid waste or hazardous waste into
or on any land or water,’’] of ccntaminants into the
groundwater [for into the environment]. Thus, the statute
neither punishes wrongdoing nor imposes liability for in-
juries inflicted by past acts. Rather, as defendants
themselves argue, its orientation is essentially prospective.
When construed in this manner, the statute is simply not
retroactive. It merely relates to current and future condi-
tions.
Id. at 1071; accord United States v. Diamond Shamrock Corp.,
17 Env’t Rep. Cases (BNA) at 1333-34; cf. United States v.
— A-28 —
South Carolina Recycling & Disposal, Inc., 20 Env’t Rep. Cases
(BNA) at 1760-61 (similar analysis of CERCLA). We hold
RCRA is not retroactive because it imposes liability for the pre-
sent and future conditions resulting from past acts. But cf.
United States v. Conservation Chemical Co., 619 F. Supp. at
220-22 (holding RCRA should be considered a retroactive law,
but finding no due process violation).
In summary, we hold that RCRA § 7003(a), 42 U.S.C.A. §
6973(a) (West Supp. 1986), as initially enacted and as clarified
by the 1984 amendments, imposes strict liability upon past off-
site generators of hazardous waste and upon past transporters
of hazardous waste. We reverse that part of the district court
judgment holding that RCRA does not apply to past non-
negligent off-site generators and transporters.
V. SCOPE OF LIABILITY
The district court found NEPACCO liable as the ‘‘owner or
operator’? of a ‘‘facility’’ (the NEPACCO plant) under
CERCLA § 107(a)(1), 42 U.S.C. § 9607(a)(1), and as a
‘*person’’ who arranged for the transportation and disposal of
hazardous substances under CERCLA § 107(a)(3), 42 U.S.C. §
9607(a)(3). 579 F. Supp. at 847. The district court found Lee
liable as a ‘‘person’’ who arranged for the disposal of hazardous
substances under CERCLA § 107(a)(3), 42 U.S.C. § 9607(a)(3),
id. at 847-48, and as an ‘‘owner or operator’’ of the NEPACCO
plant under CERCLA § 107(a)(1), 42 U.S.C. § 9607(a)(1), by
**piercing the corporate veil.’’ Jd. at 848-49. The district court
also found Michaels liable as an ‘‘owner or operator’’ of the
NEPACCO plant under CERCLA § 107(a)({1), 42 U.S.C. §
9607(a)(1). Jd. at 849.
Appellants concede NEPACCO is liable under CERCLA §
107(a)(3), 42 U.S.C. § 9607(a)(3), for arranging for the
transportation and disposal of hazardous substances at the Den-
ney farm site. Brief for Appellants at 25-26. Because NEPAC-
CO’s assets have already been liquidated and distributed to its
— A-29 —
shareholders, however, it is unlikely that the government wiil be
able to recover anything from NEPACCO.
Appellants argue (1) they cannot be held liable as ‘‘owners or
operators”’ of a ‘‘facility’’ because ‘‘facility’’ refers to the place
where hazardous substances are located and they did not own or
operate the Denney farm site, (2) Lee cannot be held individuai-
ly liable for arranging for the transportation and disposal of
hazardous substances because he did not ‘‘own or possess’’ the
hazardous substances and because he made those arrangements
as a corporate officer or employee acting on behalf of NEPAC-
CO, and (3) the district court erred in finding Lee and Michaels
individually liable by ‘‘piercing the corporate veil.’’ Appellants
have not claimed that any of CERCLA’s limited affirmative
defenses apply to them. See CERCLA’s limited affirmative
defenses apply to them. See CERCLA § 107(b)(1), (2), (3), 42
U.S.C. § 9607(b))1), (2), (3) (no liability if defendatn establishes
by preponderance of evidence that release was caused solely by
act of God, act of war, act or omission of third party other than
employee or agent or by contract only if defendant establishes
due care and precautions against foreseeable consequences
taken); see, e.g., United States v. Ward, 618 F. Supp. at 897-98;
United States v. Conservation Chemical Co., 619 F. Supp. at
203-04; see generally Developments, 99 Harv. L. Rev. at
1543-48.
The government argues Lee can be held individually liable
without ‘‘piercing the corporate veil,’’? under CERCLA §
107(a)(3), 42 U.S.C. § 9607(a)(3), and that Lee and Michaels
can be held individually liable as ‘‘contributors’’ under RCRA §
7003(a), 42 U.S.C.A. § 6973(a) (West Supp. 1986). For the
reasons discussed below, we agree with the government’s liabili-
ty arguments.°®
* Despite the findings by the district court, the government did not
seek to impose liability upon NEPACCO, Lee and Michaels under
CERCLA § 107(a)(1), 42 U.S.C. § 9607(a)(1), as the owners or
— A-30 —
A. Liability under CERCLA § 107(a)(1), 42 U.S.C. §
9607(a)(1)
First, appellants argue the district court erred in finding them
liable under CERCLA § 107(a)(1), 42 U.S.C. § 9607(a)(1), as
the ‘‘owners and operators’’ of a ‘‘facility’’ where hazardous
substances are located. Appellants argue that, regardless of
their relationship to the NEPACCO plant, they neither owned
nor operated the Denney farm site, and that it is the Denney
farm site, not the NEPACCO plant, that is a ‘‘facility’’ for pur-
poses of ‘‘owner and operator’’ liability under CERCLA §
107(a)(1), 42 U.S.C. § 9607(a)(1). We agree.
CERCLA defines the term ‘‘facility’’ in part as ‘‘any site or
area where a hazardous substance has been deposited, stored,
disposed of, or placed, or otherwise come to be located.”’
CERCLA § 101(9)(B), 42 U.S.C. § 9601(9)(B); see New York v.
Shore Realty Corp., 759 F.2d 1032, 1043 n.15 (2d Cir. 1985).
The term ‘‘facility’’ should be construed very broadly to include
‘‘virtually any place at which hazardous wastes have been
_ dumped, or otherwise disposed of.’’ United States v. Ward, 618
F. Supp. at 895 (definition of ‘‘facility’’ includes roadsides
where hazardous waste was dumped); see also United States v.
Conservation Chemical Co., 619 F. Supp. at 185 (stereotypical
waste disposal facility); New York v. General Electric Co., 592
F. Supp. 291, 296 (N.D.N.Y. 1984) (dragstrip); United States v.
Metate Asbestos Corp., 584 F. Supp. 1143, 1148 (D. Ariz. 1984)
scaulimiaeniiaaed _ *
operators of a facility where hazardous substances are located, and in
these appeals the government has expressed no opinion with respect to
‘owner and operator”’ liability under the circumstances in the present
case. Brief for Appellee at 46 n.23. The government further argues
that it is unnecessary to decide whether Michaels would also be liable
under CERCLA § 107)a)(3), 42 U.S.C. § 9607(a)(3), because RCRA §
7003(a), 42 U.S.C.A. § 6973(a) (West Supp. 1986), ‘‘so clearly fits the
circumstances of this case.’’ Brief for Appellee at 47 n.24. The
district court did not reach the question of Michaels’ liability under
CERCLA § 107(a), 42 U.S.C. § 9607(a). 579 F. Supp. at 849 n.31.
—
— A-31 —
(real estate subdivision). In the present case, however, the place
where the hazardous substances were disposed of and where the
government has concentrated its cleanup efforts is the Denney
farm site, not the NEPACCO plant. The Denney farm site is
the ‘‘facility.”’ Because NEPACCO, Lee and Michaels did not
own or operate the Denney farm site, they cannot be held liable
as the ‘‘owners or operators”’ of a ‘‘facility’” where hazardous
substances are located under CERCLA § 107(a)(1), 42 U.S.C. §
9607(a)(1).
B. Individual Liability under CERCLA § 107(a)(3), 42
U.S.C. § 9607(a)(3)
CERCLA § 107(a)(3), 42 U.S.C. § 9607(a)(3), imposes strict
liability upon ‘‘any person’’ who arranged for the disposal or
transporation for disposal of hazardous substances. As defined
by statute, the term ‘‘person’’ includes both individuals and
corporations and does not exclude corporate officers or
employees. See CERCLA § 101(21), 42 U.S.C. § 9601(21);
United Staies v. Ward, 618 F. Supp. at 894 (CERCLA); cf.
United States v. Pollution Abatement Services of Oswego, Inc.,
763 F.2d 133, 134-35 (2d Cir.) (individual liability for violation
of Rivers and Harbors Appropriation Act of 1899), cert.
denied, 106 S. Ct. 605 (1985). Congress could have limited the
statutory definition of ‘‘person’’ but chose not to do so. Com-
pare CERCLA § 101(20A), 42 U.S.C. § 9601(20A) (limiting
definition of ‘‘owner or operator’’). Moreover, construction of
CERCLA to impose liability upon only the corporation and not
the individual corporate officers and employees who are
responsbile for making corporate decisions about the handling
and disposal of hazardous substances would open an enormous,
and clearly unintended, loophole in the statutory scheme.
First, Lee argues he cannot be held individually liable for hav-
ing arranged for the transportation and disposal of hazardous
substances under CERCLA § 107(a)(3), 42 U.S.C. § 9607(a)(3),
becuase he did not personally own or possess the hazardous
alll
— A-32 —
substances. Lee argues NEPACCO owned or possessed the
hazardous substances.
The government argues Lee ‘‘possessed’’ the hazardous
substances within the meaning of CERCLA § 107(a)(3), 42
U.S.C. § 9607(a)(3), because, as NEPACCO’s plant supervisor,
Lee had actual ‘‘control’’ over the NEPACCO plant’s hazar-
dous substances. We agree. It is the authority to confrol the
handling and disposal of hazardous substances that is critical
under the statutory scheme. The district court found that Lee,
as plant supervisor, actually knew about, had immedicate super-
vision over, and was directly responsible for arranging for the
transporation and disposal of the NEPACCO plant’s hazardous
substances at the Denney farm site. We believe requiring proof
of personal ownership or actual physical possession of hazar-
dous substances as a precondition for liability under CERCLA §
107(a)(3), 42 U.S.C. § 9607(a)(3), would be inconsistent with the
broad remedial purposes of CERCLA. Cf. United States v.
Mottolo, 14 Envtl. L. Rep. (Envtl. L. Inst.) 20497, 20499
(D.N.H. 1984) (person who arranges for disposal or transporta-
tion for disposal need not own or possess the hazardous waste).
Next, Lee argues that because he arranged for the transporta-
tion and disposal of the hazardous stubstances as a corporate
officer or employee acting on behalf of NEPACCO, he cannot
be held individually liable for NEPACCO’s violations. Lee also
argues the district court erred in disregarding the corporate enti-
ty by ‘‘piercing the corporate veil’? because there was no
evidence that NEPACCO was inadequately capitalized, the cor-
porate formalities were not observed, individual and corporate
interests were not separate, personal and corporate funds were
commingled or corporate property was diverted, or the cor-
porate form was used unjustly or fraudulently.
The government argues Lee can be held individually liable,
without ‘“‘piercing the corporate veil,’’ because Lee personally
arranged for the disposal of hazardous substances in violation
— A-33 —
of CERCLA §107)a)(3), 42 U.S.C. § 9607(a)(3). We agree. As
discussed below, Lee can be held individually liable because he
personally participated in conduct that violated CERCLA; this
personal liability is distinct from the derivative liability that
results from ‘‘piercing the corporate veil.’ ‘‘The effect of pier-
cing a corporate veil is to hold the owner [of the corporation]
liable. The rationale for piercing the corporate veil is that the
corporation is something less than a bona fide independent enti-
tv.”’ Donsco, Inc. v. Casper Corp., 587 F.2d 602, 606 (3d Cir.
1978). Here, Lee is liable because he personally participated in
the wrongful conduct and not because he is one of the owners of
what may have been a less than bona fide corporation. For this
reason, we need not decide whether the district court erred in
piercing the corporate veil under these circumstances.
We now turn to Lee’s basic argument. Lee argues that he
cannot be held individually liable for NEPACCO’s wrongful
conduct because he acted solely as a corporate officer or
employee on behalf of NEPACCO. The liability imposed upon
Lee, however, was not derivative but personal. Liability was
not premised solely upon Lee’s status as a corporate officer or
employee. Rather, Lee is individually liable under CERCLA §
107(a)(3), 42 U.S.C. § 9607(a)(3), because he personally arrang-
ed for the transportation and disposal of hazardous substances
on behalf of NEPACCO and thus actually participated in
NEPACCO’s CERCLA violations.
A corporate officer is individually liable for the torts he
[or she] personally commits [on behalf of the corporation]
and cannot shield himself [or herself] behind a corporation
when he [or she] is an actual participant in the tort. The
fact that an officer is acting for a corporation also may
make the corporation vicariously or secondarily liable
under the doctrine of respondeat superior; it does not
however relieve the individual of his [or her] responsibility.
Donsco, Inc. v. Casper Corp., 587 F.2d at 606 (citations omit-
ted); see New York v. Shore Realty Corp., 759 F.2d at 1052-53
— << oa
(CERCLA; New York law); United States v. © onservation,
Chemical Co., 619 F. Supp. at 187-90 (CERCLA); United
States v. Carolawn Cc., 14 Envtl. L. Rep. (Envtl. L. Inst.)
10699, 20700 (D.S.C. 1984) (CERCLA); United States v. Mot-
tolo, 14 Envtl. L. Rep. (Envtl. L. Inst.) at 20499; cf. United
States v. Pollution Abatement Services of Oswego, Inc., 763
F.2d at 135 (corporate officers liable for violating Rivers and
Harbors Appropriations Act of 1899); see also Escude Cruz v.
Ortho Pharmaceutical Corp., 619 F.2d 902, 907 (ist Cir. 1980)
(general discussion of liability of corporate officers for par-
ticipation in corporate torts), citing Lobato v. Pay Less Drug
Stores, Inc., 261 f.2d 406, 408-09 (10th Cir. 1958); see generally
3A W. Fletcher, Cyclopedia of the Law of Private Corporations
§ 1135 (rev. perm. ed. 1986). Thus, Lee’s personal involvement
in NEPACCO’s CERCLA violations made him individually
liable.
C. Individual Liability under RCRA § 7003(a), 42
U.S.C.a. § 6973(a) (West Supp. 1986)
The district court did not reach the question of individual
liability under RCRA because it concluded that RCRA did not
impose liability upon past non-negligent off-site generators like
NEPACCO. As we discussed in Part IV, RCRA is applicable to
past non-negligent off-site generators. The government argues
Lee and Michaels are individually liable as ‘‘contributors’’
under RCRA § 7003(a), 42 U.S.C.A. § 6973(a) (West Supp.
1986). We agree.
RCRA § 7003(a), 42 U.S.C.A. § 6973(a) (West Supp. 1986),
imposes strict liability upon ‘‘any person’’ who is contributing
or who has contributed to the disposal of hazardous substances
that may present an imminent and substantial endangerment to
health or the environment. As defined by statute, the term
**person’’ includes both individuals and corporations and does
not exclude corporate officers and employees. See RCRA §
1004(15), 42 U.S.C. § 6903(15); cf. United States v. Johnson &
————eE
— A-35 —
Towers, Inc., 741 F.2d 662, 665-66 (3d Cir. 1984) (employees
could be criminally prosecuted for RCRA violations), cert.
denied, 469 U.S. 1208 (1985); United States v. Ward, 676 F.2d
94, 97 (4th Cir.) (chairperson of board convicted of unlawful
disposal of toxic substances in violation of 15 U.S.C. §§ 2605,
2614, and 40 C.F.R. § 761.01(b)), cert. denied, 459 U.S. 835
(1982). As with the CERCLA definition of ‘‘person,’’ Congress
could have limited the RCRA definition of ‘‘person’’ but did
not do so. Compare CERCLA § 101(20A), 42 U.S.C. §
9601(20A)} (limiting definition of ‘‘owner and operator’’). More
importantly, imposing liability upon only the corporation, but
not those corporate officers and employees who actually make
corporate decisions, would be inconsistent with Congress’ in-
tent to impose liability upon the persons who are involved in the
handling and disposal of hazardous substances. See United
States v. Price, 523 F. Supp. at 1073; see also H.R. Conf. Rep.
No. 1133, 98th Cong., 2d Sess. 119, reprinted in 1984 U.S. Code
Cong. & Ad. News at 5690; S. Rep. No. 172, 96th Cong., 2d
Sess. 5, reprinted in 1980 U.S. Code Cong. & Ad. News 8665,
8669.
Our analysis of the scope of individual liability under the
RCRA is similar to our analysis of the scope of individual
liability under CERCLA. NEPACCO violated RCRA §
7003(a), 42 U.S.C.A. § 6973(a) (West Supp. 1986), by ‘‘con-
tributing to’’ the disposal of hazardous substances at the Den-
ney farm site that presented an imminent and substantial en-
dangerment to health and the environment. Thus, Lee and
Michaels can be held individually liable if they were personally
involved in or directly responsible for corporate acts in violation
of RCRA. Cf. United States v. Pollution Abatement Services
of Oswego, Inc., 763 F.2d at 134 (corporate officers and
shareholders individually liable for company discharging refuse
into creek in violation of Rivers and Harbors Appropriations
Act of 1899); United States v. Johnson & Towers, Inc., 741
F.2d at 664-66 (employees criminally liable for RCRA viola-
tions).
hi —
We hold Lee and Michaels are individually liable as ‘‘con-
tributors’’ under RCRA § 7003(a), 42 U.S.C.a. § 9673(a) (West
Supp. 1986). Lee actually participated in the conduct that
violated RCRA; he personally arranged for the transporation
and disposal of hazardous substances that presented an immi-
nent and substantial endangerment to health and the environ-
ment. Unlike Lee, Michaels was not personally involved in the
actual decision to transport and dispose of the hazardous
substances. As NEPACCO’s corporate president and as a ma-
jor NEPACCO shareholder, however, Michaels was the in-
dividual in charge of and directly responsible for all of NEPAC-
CO’s operations, including those at the Verona plant, and he
had the ultimate authority to control the disposal of NEPAC-
CO’s hazardous substances. Cf. New York v. Shore Realty
Corp., 759 f.2d at 1052-53 (shareholder-manager held liable
under CERCLA).
In summary, we hold Lee individually liable for arranging for
the transportation and disposal of hazardous substances in
violation of CERCLA § 107(a)(3), 42 U.S.C. § 9607(a)(3), and
Lee and Michaels individually liable for contributing to an im-
minent and substantial endangerment to health and the environ-
ment in violation of RCRA § 7003(a), 42 U.S.C.A. § 6973(a)
(West Supp. 1986).
VI. CAPACITY OF NEPACCO TO BE SUED
The capacity of a corporation to sue or be sued is determined
by the law under which it is organized. Fed. R. Civ. P. 17(b).
The district court held, under Delaware law, ‘‘a corporation
with a forfeited charter is not completely dead for all purposes,
but merely in ‘a state of coma,’ during which it is still subject to
suit, even if the suit is brought more than three years after the
charter forfeiture.’’ 579 F. Supp. at 827 n.1, citing Ross v.
Venezuelan-American Independent Oil Producers Ass’n, 230 F.
Supp. 701 (D. Del. 1964), and Wax v. Riverview Cemetery Co.,
41 Del. (2 Terry) 424, 24 A.2d 431 (Super. Ct. 1942).
— A-37 —
Appeliants argue the district court erred in holding that under
Delaware law NEPACCO had the capacity to be sued. Ap-
pellants argue NEPACCO did not have the capacity to be sued
because the government’s action was not brought against
NEPACCO until 1980, more than three years after NEPACCO
had ceased to do business (1972), had liquidated its assets
(1974), and had forfeited its charter for failure to nominate a
successor registered agent (1976). See Del. Code Ann. tit. 8, §
278. Appellants admit that NEPACCO has failed to file a cer-
tificate of voluntary dissolution with the Delaware Secretary of
State, but they argue that NEPACCO simply no longer exists as
a corporate entity. Appellants argue that under Delaware law
the three-year period begins to run after either dissolution or
forfeiture, citing Frederic G. Krapf & Son, Inc. v. Gorson, 243
A.2d 713, 715 (Del. Super. Ct. 1968).
The government argues the district court correctly held that
under Delaware law NEPACCO had the capacity to be sued.
The government argues that forfeiture of the corporate charter
and voluntary dissolution are not equivalent and that under
Delaware law a corporation whose charter has been forfeited
has not in fact been dissolved, but instead is merely in a
suspended state from which it can be revived at any time.
Although the language in Frederic G. Krapf & Son, Inc. v.
Gorson, id. at 714, suggest that forfeiture and dissolution may
be comparable for purposes of Del. Code Ann. tit. 8, § 278, we
agree with the district court that forfeiture of the corporate
charter and voluntary dissolution of the corporation are not
legally equivalent. The cases distinguishing forfeiture from
dissolution are preoccupied with preserving the marketability of
titles; however, the case law does support the district court’s
analysis distinguishing forfeiture from voluntary dissolution. In
the key case, Wax v. Riverview Cemetery Co., a holding com-
pany had mortgaged certain property it owned. The holding
company then conveyed the property and mortgage to a third
party. The holding company’s charter was then revoked for
— A-38 —
nonpayment of taxes. Nine years iater the mortgage foreclosed
on the property and bought it at a judicial sale. When the mor-
tgagee later sold the property, the prospective buyer chailenged
the marketability of the mortgagee’s title. The state court held
that forfeiture of the holding company’s charter for nonpay-
ment of taxes ‘‘does no more than forfeit the corporate right to
do business, but does not extinguish the corporation as a legal
entity,’’ and, therefore, the holding company could still ‘‘serve
as [a] repository of title and as [an] obligor of a debt.’’ 24 A.2d
at 436. Accord Ross v. Venezuelan-American Independent Oil
Producers Ass’n, 230 F. Supp. at 703-04 (federal district court
for the District of Delaware interpreting Delaware law); see
generally 16A W. Fletcher, Cyclopedia of the Law of Private
Corporations ch. 65 (rev. perm. ed. 1979). But cf. Johnson v.
Helicopter & Airplane Services Corp., 404 F. Supp. 726, 730-35
(D. Md. 1975) (overview of Delaware and federal cases; holding
that a corporation that had been dissolved, even though it was
still conducting certain proceedings brought during its winding-
up period, had lost its capacity to sue and be sued and thus
could not be sued more than three years after dissolution).
Here, NEPACCO has lost its charter, but it has not been
dissolved. We agree with the district court that, under these cir-
cumstances, NEPACCO’s charter can be ‘‘revived’’ and that it
has the capacity to be sued even though the government’s initial
complaint was not filed until more than three years after
forfeiture.
Vil. BURDEN OF PROOF OF RESPONSE COSTS
The district court found appellants had the burden of proving
the government’s response costs were inconsistent with the
NCP, 579 F. Supp. at 580, and that response costs that are not
inconsistent with the NCP are conclusively presumed to be
reasonable and therefore recoverable, id. at 851. Appellants
argue the district court erred in requiring them to prove the
response costs were inconsistent with the NCP, not cost-
v SR:
— A-39 —
effective or unnecessary. Appellants further argue the district
court erred in assuming all costs that are consistent with the
NCP are conclusively presumed to be reasonable. Appellants
note that the information and facts necessary to establish con-
sistency with the NCP are matters within the possession of the
governmient.
We believe the district court’s analysis is correct. CERCLA §
107(a)(4)(A), 42 U.S.C. § 9607({a)(4)(A), states that the govern-
ment may recover from responsible parties ‘‘all costs of removal
or remedial action . . . not inconsistent-with the [NCP].’’ The
statutory language itself establishes an exception for costs that
are inconsistent with the NCP, but appellants, as the parties
claiming the benefit of the exception, have the burden of prov-
ing that certain costs are inconsistent with the NCP and,
therefore, not recoverable. See United States v. First City Na-
tional Bank, 386 U.S. 361, 366 (1967). Contrary to appellants’
argument, ‘‘not inconsistent’’ is not, at least for purposes of
statutory construction and not syntax, the same as
‘*consistent.’’ See, e.g., United States v. Ward, 618 F. Supp. at
899; United States v. Conservation Chemical Co., 619 F. Supp.
at 186; Lone Pine Steering Comm. v. EPA, 600 F. Supp. 1487,
1499 (D.N.J.), aff’d, 777 F.2d 882 (3d Cir. 1985), cert. denied,
106 S. Ct. 1970 (1986); New York v. General Electric Co., 592
F. Supp. at 303-04 (state action for recovery of response costs);
J.V. Peters & Co. v. Ruckelshaus, 584 f. Supp. 1005, 1010
(N.D. Ohio 1984), aff’d, 767 F.2d 263 (6th Cir. 1985).
The statutory scheme also supports allocation of the burden
of proof of inconsistency with the NCP upon the defendants
when the government seeks recovery of its response costs. As
noted above, CERCLA § 107(a)(4)(A), 42 U.S.C. §
9607(a)(4)(A), provides that the federal government or a state
can recover ‘‘all costs of removal or remedial action . . . not in-
consistent with the [NCP].’’ In comparison, CERCLA §
107(a)(4)(B), 42 U.S.C. § 9607(a)(4)(B), provides that ‘‘any
other person,’’ referring to any ‘‘person’’ other than the federal
ee ee TS
—_ va
governement or a state, can recover ‘‘any other necessary costs
of response . . . consistent with the [NCP].’’ That statutory
language indicates that nongovernmental entities must prove
that their response costs are consistent with the NCP in order to
recover them. The statutory scheme thus differentiates between
governmental and nongovernmental entities in allocating the
burden of proof of whether resonse costs are consistent with the
NCP. See, e.g., United States v. Ward, 618 F. Supp. at 899;
New York v. General Electric Co., 592 F. Supp. at 303-04 (state
action for recovery of response costs).
The statutory language also supports the district court’s
reasoning that under CERCLA § 107(a)(4)(A), 42 U.S.C. §
9607(a)(4)(A), ‘‘all costs’’ incurred by the government that are
not inconsistent with the NCP are conclusively presumed to be
reasonable. CERCLA does not refer to ‘‘all reasonable costs”’
but simply to ‘‘all costs.’’ Cf. Federal Water Pollution Control
Act § 311(f) (FWPCA), 33 U.S.C. § 1321(f) (responsible parties
are liable for ‘‘actual costs incurred’’ by the government for
cleanup); see, e.g., Union Petroleum Corp. v. United States,
228 Ct. Cl. 54, 651 F.2d 734, 744 (1981) (construing ‘‘actual
costs incurred’’ in 33 U.S.C. § 1321(f) to apply conclusive
presumption of reasonableness). Case law interpreting the
FWPCA is relevant because CERCLA defines the NCP by
referring to the NCP mandated by the FWPCA. CERCLA §§
101(31), 105, 42 U.S.C. §§ 9601(31), 9605; see United States v.
Conservation Chemical Co., 619 F. Supp. at 204 (noting cross-
references in CERCLA to FWPCA); United States v. Shell Oil
Co., 605 F. Supp. at 1073-74 & n.4 (the NCP as revised to incor-
porate CERCLA was issued in 1982).’
’ The 1982 NCP, 40 C.F.R. § 300.1-.86 (1985), was revised effective
Feb. 18, 1986, 50 Fed. REg. 47,912-79 (1985).
i ee Ri ine Wt FN Recline, Will tell Wee 9 eR dia” che ln se
~ ft x
Appellants also argue the district court erred in requiring
them to establish that the government’s cleanup actions were
cost-effective and necessary. This argument challenges the
government’s choice of a particular cleanup method. We note,
however, that CERCLA § 105(3), (7), 42 U.S.C. § 9605(3), (7),
requires the EPA, as the agency designated by the President, to
revise the NCP required by § 311 of the FWPCA, 33 U.S.C. §
1321, to include the ‘‘national hazardous substance response
plan,’’ which is specifically required by CERCLA to include
‘*tncihods and criteria for determining the appropriate extent of
removal, remedy, and other measures,’’ and ‘‘means of assur-
ing that remedial action measures are cost-effective.’’ Con-
sideration of whether particular action is ‘‘necessary’’ is thus
factored into the ‘‘cost-effective’’ equation. The term ‘“‘cost-
effective’ is defined by regulation as ‘‘the lowest cost alter-
native that is technologically feasible and reliable and which ef-
fectively mitigates and minimizes damage to and provides ade-
quate protection of public health, welfare, or the
environment.’’ 40 C.F.R. § 300.68(j) (1986).
Because determining the appropriate removal and remedial
action involves specialized knowledge and expertise, the choice
of a particular cleanup method is a matter within the discretion
of the EPA. The applicable standard of review is whether the
agency’s choice is arbitrary and capricious. As explained in
United States v. Ward,
{i]f [appellants] wish the court to review the consistency of
[the government’s] actions with the NCP, then they are
essentially alleging that the EPA did not carry out its
statutory duties. The statute provides liability except for
costs ‘‘not inconsistent’’ with the NCP. This language re-
quires deference by this court to the judgement of agency
professionals. [Appellants], therefore, may not seek to
have the court substitute its own judgment for that of the
EPA. [Appellants] may only show that the EPA’s decision
about the method of cleanup was “‘inconsistent’’ with the
od
—s
NCP in that the EPA was arbitrary and capricious in the
discharge of their duties under the NCP.
618 F. Supp. at 900.
Here, appellants failed to show that the government’s
response costs were inconsistent with the NCP. Appellants also
failed to show that the EPA acted arbitrarily and capriciously in
choosing the particular method it used to clean up the Denney
farm site.
Vill. REDUCTION OF AWARD BY AMOUNT OF PRIOR
SETTLEMENT
Appellants next argue the district court erred in refusing to
reduce the amount of its judgment by $100,000, the amount
paid by Syntex pursuant to the settlement and consent decree in
September 1980. Appellants argue that unless the judgment is
offset by the amount of the Syntex settlement, the government
will improperly receive a double recovery of that amount from
Syntex and appellants. Thus, appellants argue the district court
should have reduced the awrd by $100,000.
The government argues the district court correctly refused to
reduce the award by the amount of the Syntex settlement. We
agree. According to the government’s exhibits, the government
did not seek a double recovery. The government had incurred
response costs of $494,639.54 through March 10, 1983, but
sought recovery from appellants of only $394.639.54, or the
total amount of its response costs tc date reduced by the
$100,000 Syntex settlement, plus future response costs. Thus,
the government sought to recover from appellants an amount
that had already been reduced to reflect the amount of the
Syntex settlement.
IX. DEMAN® FOR JURY TRIAL
Appellants next argue the district court erred in denying their
demand for a jury trial because the government’s action for
re
at Se li.
— ©:
recovery of its response costs under CERCLA and RCRA was
essentially a claim for legal damages. We disagree. When the
government seeks recovery of its response costs under CERCLA
or its abatement costs under RCRA, it is in effect seeking
equitable relief in the form of restitution or reimbursement of
the costs it expended in order to respond to the health and en-
vironmental danger presented by hazardous substances. See,
e.g., United States v. Price, 688 F.2d at 213-14 (reimbursement
of abatement costs under RCRA as equitable relief); United
States v. Mottolo, 605 F. Supp. at 912-13 (citing seven cases, in-
cluding NEPACCO, that characterize recovery of response
costs under CERCLA as equitable relief); see generally
Developments, 99 Harv. L. Rev. at 1492 & nn.46, 47. The
district court correctly found appellants did not have a right to a
jury trial of claims for equitable relief. See Ross v. Bernhard,
396 U.S. 531, 533 (1970).
X. CONCLUSION
In conclusion, we hold (1) CERCLA applies retroactively, (2)
the government can recover its pre-enactment response costs
under CERCLA, (3) RCRA imposes strict liability upon past
off-site generators and transporters of hazardous substances,
(4) Lee and Michaels can be held individually liable, (5)
NEPACCO had the capacity to be sued, (6) appellants had the
burden of proving the government’s response costs were incon-
sistent with the NCP, (7) the government’s award shouid not be
reduced by the Syntex settlement, and (8) appellants did not
have the right to a jury trial.
Accordingly, the judgment of the district court is affirmed in
part, reversed in part and remanded for further proceedings
consistent with this opinion. The district court’s refusal to
dismiss NEPACCO as a party cefendant, retroactive applica-
tion of CERCLA to pre-enacinient conduct, imposition of in-
dividual liability upon corporate officers who actually control
the handling and disposal of hazardous substances, placement
—_-' oo
upon the responsible parties of the burden of proof that the
government’s response costs are inconsistent with the NCP,
refusal to reduce the award by the amount of the prior settle-
ment, and denial of a jury trial are affirmed. The district
court’s refusal to allow the government to recover its response
costs incurred before the enactment of CERCLA in 1980,
refusal to impose strict liability upon past off-site generators
and transporters of hazardous substances under RCRA §
7003(a), 42 U.S.C.A. § 6973(a) (West Supp. 1986), and imposi-
tion of liability upon appellants as owners or operators of a
facility pursuant to CERCLA § 107(a)(1), 42 U.S.C. §
9607(a)(1), are reversed.
On remand, before awarding a specific amount of pre-
enactment response costs to the government under CERCLA,
the district court should afford appellants an opportunity to
show that the government’s pre-enactment response costs were
inconsistent with the NCP. Alternatively, because the govern-
ment also sought to recover the response costs it incurred before
the enactment of CERCLA in the form of equitable relief as
abatement costs under RCRA, on remand the district court
could grant the government recovery of such costs as a matter of
equitable discretion.
JOHN R. GIBSON, Circuit Judge, concurring in part and dis-
senting in part.
I concur with the court’s opinion except for parts IV-A, IV-B,
and V-C, holding that RCRA § 7003(a), 42 U.S.C. § 6973(a)
(1982), imposes liability on past off-site nonnegligent generators
and transporters and determining that the government could
recover its response costs from Lee and Michaels under section
7003(a). I respectfully dissent from the court’s opinion as to
those points.
The majority’s analysis of liability under the RCRA focuses
exclusively on the legislative history of the 1984 amendments to
the RCRA. The majority particularly rely on House Con-
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At Mabaso
BPRS Nec
— A-45 —
ference Report No. 1133, which singles out the district court’s
opinion and states that it is ‘‘inconsistent with the authority
conferred by \section 7003] as initially enacted and with these
clarifying amendments.’’ H.R. Conf. Rep. No. 1133, 98th
Cong., 2d Sess. 119 (1984), reprinted in 1984 U.S. Code Cong. &
Ad. News 5649, 5690. The Conference Report also states that
section 7003 ‘‘has always’’ reached nonnegligent generators and
transporters. Jd. From these statements, the majority conclude
that ‘‘the 98th Congress made clear that the intention of the
94th Congress in enacting the RCRA in 1976 had been to impose
liability upon past nonnegligent off-site generators and
transporters of hazardous waste.’’ Ante at 27. Thus, the ma-
jority hold that the RCRA as it read prior to the 1984 amend-
ments imposed strict liability upon past generators and
transporters and that the district court erred in holding that pro-
of of fault or negligence was necessary for the government to
recover its response costs under the RCRA. Ante at 26-27.
1 think that the 1984 House Conference Report is nothing
more than a blatant effort by members of a later Congress to
graft their personal views of the scope of liability under the
RCRA onto the original act. It is bootstrapping, and the ma-
jority fail to recognize it as such. The Conference Report
characterizes the 1984 amendments as ‘‘clarifying’’ the RCRA.
The ‘‘clarifying’’ amendments to section 7003, however, did not
alter the crucial phrase ‘‘contributing to,’’ the construction of
which the majority acknowledge as ‘‘the critical issue,’’ ante at
21, other than to cast it in both the present and the past tense:
**has contributed to or * * * is contributing.’’ 42 U.S.C.A. §
6973(a) (West Supp. 1986). Nor do the amendments supply a
definition for this phrase. The amendments to section 7003(a)
are directed toward changing the scope of the section to reach
past as well as present and future generators and transporters of
hazardous waste. I believe this to be a substantive change,
rather than a clarification. In any event, because the amend-
ments did not relate to the ‘‘contributing to’’ language, the
statements in the House Conference report regarding the stan-
—~
dard cf liability under section 7003(a)—negligence versus strict
liability—are wholly gratuitous.
‘T]he views of a subsequent Congress form a hazardous
basis for inferring the intent of an earlier one.’’ United States v.
Price, 361 U.S. 304, 313 (1960). ‘‘[S]Juch ‘[ljegislative observa-
tions. . .are in no sense part of the legislative history.’ ‘It is the
intent of the Congress that enacted [the section] . . . that con-
trols.’ ’? Oscar Mayer & Co. v. Evans, 441 U.S. 750, 758 (1979)
(quoting United Airlines, Inc. v. McMann, 434 U.s. 192, 200
n.7 (1977), and Teamsters v. United States, 431 U.S. 324, 354
n.39 (1977)). Moreover, the Supreme Court has observed that
‘*subsequent legislative history will rarely override a reasonable
interpretation of a statute that can be gleaned from its language
and legislative history prior to its enactment.’’ Consumer Pro-
ducts Safety Commission v. GTE Sylvania, 447 U.S. 102, 118
n.13 (1980). This court has also recently acknowledged the
dubious value of subsequent legislative history. See Citizens
State Bank of Marshfield v. FDIC, 751 F.2d 209, 217 (1984).
Applying these principles to the district court’s interpretation of
the RCRA and its legislative history, I would affirm its
resonable conclusion that Congress did not intend to impose
strict liability on past generators and transporters of hazardous
waste. I would not accept at face value the assertion by certain
members of the 98th Congress that they can divine the intent of
the 94th Congress in enacting the RCRA some eight years
earlier.
I recognize that the substance of the 1984 amendments may
have a bearing on this case. The district court did not have
before it the amendments or their associated legislative
materials. As a general rule we are to apply the law in effect at
the time we render our decision. See, e.g., Bradley v. Richmond
School Board, 416 U.S. 696, 711 (1974). The majority purport
to base their decision on the RCRA as it existed prior to the 1984
amendments, however, and agree with the House Conference
Report that the i984 amendments, merely ‘‘clarified’’ the scope
— A-47 —
of liability under the RCRA. Ante at 28. I differ. I have
already observed that I believe the 1984 amendments
significantly altered the scope of liability under the RCRA. I
think that the parties should at least be given the opportunity to
develop their factual and legal contentions as to the effect of
and in light of the 1984 amendments before the district court
and thus present the issue more squarely for our consideration,
if appealed.
I also disagree with the majority’s determination that Lee and
Michaels are liable under section 7003(a) for the government’s
response costs as generators and transporters. The district court
did not reach this issue, as it concluded that RCRA liability did
not extend to past nonnegligent generators and transporters of
hazardous waste. The majority, however, both reverse the
district court’s legal conclusion and then find as a factual matter
that Lee and Michaels are liable. Ante at 36-37. This type of
factfinding is clearly the province of the district court, and
remanding the question of liability to the district court is more
appropriate than the course of action taken by the court today.
Missouri Pacific Joint Protective Board v. Missouri Pacific
Railroad Co., 730 F.2d 533, 537 (8th Cir. 1984).
al a a ore
No hee
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64M Ose
A true copy.
Attest:
Clerk, U.S. Court of Appeals, Eighth Circuit.
—_—
APPENDIX B
UNITED STATES COURT OF APPEALS
FOR THE EIGHTH CIRCUIT
Nos. 84-1837/1853WM
United States of America,
Appellee/Cross-Appellant,
Vv.
Northeastern Pharmaceutical & Chemical Co.,
Inc., etc., et al.,
Appellants/Cross-Appellees.
Ronald Mills and Syntex Agri-business, Inc.
Appeal and Cross-appeal from the United States
District Court for the Western District of Missouri.
JUDGMENT
These appeals from the United States District Court were sub-
mitted on the record of the said district court, briefs of the par-
ties and were argued by counsel.
Upon consideration of the premises, it is hereby adjudged
and decreed that the judgment of the district court is affirmed in
part, reversed in part and remanded for further proceedings
consistent with the opinion of this Court.
December 31, 1986
Appellee/Cross-Appellant will recover from appellants/cross-
appellees the sum of $117.30.
Order entered in accordance with opinion.
/s/ Robert D. St. Vrain
Clerk, U.S. Court of Appeals, 8th Circuit.
— Ad —
APPENDIX C
UNITED STATES COURT OF APPEALS
FOR THE EIGHTH CIRCUIT
Nos. 84-1837/1853WM
United States of America,
Appellant/Cross-Appellant,
Vv.
Northeastern Pharmaceutical & Chemica! Co., Inc.,
etc., et al.,
Appellants/Cross-Appellees.
Appeals from the United States District Court
for the Western District of Missouri.
Appellants/Cross-Appellees’ petition for rehearing en banc
has been considered by the Court and is denied.
Judges John R. Gibson and Theodore McMillian would have
granted the petitions. Judge Arnold declined to participate in
the voting.
Petition for rehearing by the panel is also denied.
April 8, 1987
Order entered at the Direction of the Court:
Clerk, U. S. Court of Appeals, Eighth Circuit.
— A-50 — :
APPENDIX D
IN THE UNITED STATES DISTRICT COURT FOR THE
WESTERN DISTRICT OF MISSOURI
SOUTHERN DIVISION
No. 80-5066-CV-S-4
United States of America,
Plaintiff,
VS.
Northeastern Pharmaceutical and Chemical
Company, Inc., et al.,
Defendants.
MEMORANDUM OPINION
The plaintiff instituted this action on August 1, 1980 and filed
an amended complaint on August 19, 1982 seeking injunctive
relief and reimbursement of al! costs incurred in performing cer-
tain remedial and removal a«tions at the Denney farm site, near
Verona, Missouri, pursuant to section 7003 of the Resource
Conservation and Recovery Act (RCRA), 42 U.S.C. § 6973, and
sections 104, 106(a) and 107(a) of the Comprehensive En-
vironmental Response, Compensation, and Liability Act
(CERCLA), 42 U.S.C. §§ 9604, 9606(a) and 9607(a). The Court
has jurisdiction over this action pursuant to 28 U.S.C. § 1345;
42 U.S.C. § 6973, and 42 U.S.C. §§ 9604, 9606(a), and 9613(b).
Summary of Issues
The Court considered the following issues:
1. Whether section 7003 of RCRA or sections 104, 106(a) and
107(a) of CERCLA apply retroactively to hold past non-
negligent off-site generators and transporters liable for the costs
incurred in the cleanup of an inactive or abandoned hazardous
waste disposal site?
— A-51 —
2. Whether sections 104, 106(a) and 107(a) of CERCLA app-
ly retroactively to hold past non-negligent off-site generators
and transporters liable for response costs incurred prior to the
~ enactment of CERCLA?
3. If CERCLA is to be applied retroactively, does it violate
the Fifth Amendment Due Process Clause of the United States
Constitution?
4. What standard of liability should be imposed under
CERCLA — strict liability or negligence?
5. If the defendants are liable, whether joint and several
liability should be imposed?
6. Whethe; the Denney farm disposal site presented an immi-
nent and substantial endangerment to the public health or
welfare or the environment because of an actual or threatened
release of a hazardous substance from the site?
7. Whether these specific defendants are liable under the pro-
visions of CERCLA?
8. If the defendants are liable under CERCLA, what costs
are recoverable by plaintiff?
Summary of Conclusions of Law
The Court finds that:
1. Section 7003 of RCRA does not apply retroactively to past
non-negligent off-site generators and transporters.
2. Sections 104, 106(a) and 107(a) of CERCLA do apply
retroactively to past non-negligent off-site generators and
transporters.
3. Sections 104, 106(a) and 107(a) of CERCLA do not apply
retroactively to response costs incurred prior to December 11,
1980.
— A-52 —
4. CERCLA does not violate the Fifth Amendment Due Pro-
cess Clause.
5. The standard to be applied in determining liability under
CERCLA is strict liability.
6. CERCLA ailows for the imposition of joint and several
liability.
7. The Denney farm site presented an imminent and substan-
tial endangerment to the public health, welfare and the environ-
ment.
8. All four defendants are jointly and severally liable pur-
suant to CERCLA for all costs for salaries, expenses and at-
torney fees.
9. All four defendants are jointly and severally liable for pre-
judgment interest at the rate of 9% per annum calculated from
August 19, 1982, as well as, all future costs of removal or
remedial actions incurred by the plaintiff not inconsistent with
the national contingency plan.
\
INITIAL FINDINGS OF FACT
Defendant Northeastern Pharmaceutical and Chemical Co.,
Inc. (NEPACCO) is a corporation incorporated in 1966 under
the laws of Delaware with its principal office in Stamford, Con-
necticut. NEPACCO’s corporate charter was forfeited by the
Delaware-Secretary of State on August 22, 1976, for failure to
maintain an agent for service of process. NEPACCO never fil-
ed a certificate of voluntary dissolution with the Delaware
Secretary of State, although in 1974 its assets were liquidated
and the proceeds distributed to shareholders after payment of
the corporation’s outstanding debts.' Defendant Edwin B.
Michaels (Michaels) formed NEPACCO, held stock in the cor-
poration, and was its president. Defendant John W. Lee (Lee)
was the vice-president of NEPACCO and was also a
stockholder. Defendant Ronald Mills (Mills) was employed by
fd aetanX
~— :
NEPA“CCO at the Verona, Missouri plant as shift supervisor.
Defendant Syntex Agribusiness, Inc. (Syntex) is a corporation
incorporated in the State of Delaware and doing business in the
State of Missouri.
The NEPACCO Manufacturing Process
On June 7, 1967, defendani Michaels applied for a patent on
a method of manufacturing hexachlorophene. On February 6,
1968, defendants Michaels and Lee applied for a patent on a
method for purifying 2, 4, 5-trichlorophenol (TCP) and hex-
achlorophene. On or about November 18, 1969, NEPACCO
entered into an agreement with Hoffman-Taff, Inc., whereby
NEPACCO leased portions of the premises at an existing
manufacturing facility located near Verona, Missouri, and pur-
chased manufacturing equipment used by Hoffman-Taff and
located therein for the purpose of manufacturing hex-
achlorophene. Hoffman-Taff had manufactured the com-
pound known as agent orange prior to their closure and subse-
quent sell-out to Syntex. NEPACCO manufactured hex-
achlorophene at the Verona facility from April 1970 to January
1$72. Michaels was present at the Verona facility on a perma-
nent basis during the first year of operation and construction
(1970) and during that time had overall responsibility for com-
pany operations with the upper level employees reporting to
him. By early 1971, Michaels had moved back to the state of
Connecticut leaving the direct management responsibility for
the NEPACCO plant operation and for quality control with
Lee.
The process by which NEPACCO manufactured hex-
achlorophene involves two steps: First, the production of
2,4,5-Trichlorophenol (TCP) and second, the production of the
finished product, hexachlorophene. The first step in the pro-
duction of hexachlorophene involved a reaction to form a crude
intermediate TCP. This reaction involved a dist#tlation process
resulting in refined TCP as the distillate. 2,3,7,8-tetrachloro-
— A-54 —
benzo-p-dioxin (dioxin or TCDD), among other chemicals, was
formed as a by-product in the TCP process. The residue or
waste that resulted from the TCP distillation is called still bot-
toms, described as a ‘“‘dark oily sludge.’’ The highest concen-
trations of dioxin are found in the still bottoms. Still bottoms
were removed from the process every 3rd or 4th batch and
transferred to a 7,500 galion holding tank that was located on
the west side of the piant. The holding tank was periodically
emptied by waste haulers, who carried the still bottom residue
away in tank trunks.
The second step of the production process involved the reac-
tion of the refined TCP with sulfuric acid to form hex-
achlorophene as a precipitate. Toluene and water were then ad-
ded to this crude extraction. Decolorizing and filtering clays
were added to extract the undesirable shades of color and other
impurities, one of which was dioxin. The finished product was
hexachlorophene that resembled ‘‘white flour.’’ Waste streams
from the second step included: waste solvents; recrop liquor re-
maining after the hexachlorophene had been precipitated; clay
filter cake and waste water from both steps of the process as
well as from general maintenance and cleaning.
Dioxin may have been found in each waste stream. TCP,
TCB and Toluene may have been found in the waste solvents,
contaminated waste water and clay filter cake. Hex-
achlorophene may have been found in the recrop liquor and
clay filter cake. Depending upon the efficiency of the produc-
tion system, the refined TCP may have contained dioxin that
was passed on into the hexachlorophene process. Accordingly,
the more efficient a system, the less dioxin contained in the
refined TCP, if any. If tae refined TCP did contain dioxin,
then the dioxin would have been found in the following
materials, listed in high to low concentration priority: clay filter
cake, finished hexachlorophene and waste water. The industry
standard in 1971 for levels of dioxin in refined TCP was one
part per million (ppm). The process and equipment used by
— A-55 —
NEPACCO in 1971 met industry standa.ds and it was con-
ceivable that if the NEPACCO process was continuously effi-
cient the level of dioxin ‘ound in the refined TCP would have
been below | p.p.m.
Michaels and Lee knew that the NEPACCO manufacturing
process produced by-products that contained toxic substances,
including dioxin, that could be harmful to human health. Ap-
parently, Michaels and Lee had meetings with the NEPACCO
employees to inform them of the possible dangerous toxic
substances and procedures to avoid and remedy exposure to
these substances.
Unfortunately, the NEPACCO process was not without
mishap. On on:: occasion the 7,500 gallon waste storage tank
was filled to capacity and the overflow (still bottoms) was put in
four (4) bung type 55-gallon drums that were sealed and marked
with orange or red paint. Bill Ray (plant manager) testified that
once the storage tank was emptied by the tank truck haulers, the
still bottoms contained in the four bung-type barrels were
pumped back into the 7,500 gallon storage tank. On two or
three occasions the lines to the 7,500 storage tank became block-
ed necessitating a clean-out operation. On occasion, during
these clean-out operations, a small portion of the line spilled on-
to the floor of the plant and the employees performing the
operation. Ray recited one such incident in which he was
sprayed with a fine mist by approximately one and a half to two
gallons of the substance. Ray immediately showered and took
other precautionary steps. The residue and waste from these
cleanup operations were placed in trash cans and subsequently
taken to the sanitary land fill. Ray testified that he has suffered
n> ill effects from this incident.
In March of 1971 there was a fire at the NEPACCO plant that
resulted in the destruction of at least two batches of reactants in
the hexachlorophene production phase of the process. Due to
extensive damage, the plant was closed down for several weeks
— A-56 —
in order to clean up the residue, waste and damaged equipment
created by the fire. Some of the substances contained in the
production lines were saved and reused. During the summer of
1971, Lee and Ray initiated a major plant cleanup. The waste
and residue from the major cleanup were stored in the waste
storage area northwest of the plant building. This storage area
also contained refuse and wastes that had accumulated since the
opening of the plant.
NEPACCO used black drums with lids fastened by metal
rings for disposal of waste. According to the testimony,
Hoffman-Taff had used green and white drums to hold wastes
and several of these green and white drums remained on the
plant property after Hoffman-Taff ceased operations. Defen-
dant Lee testified that he originally noticed some of these green
and white drums stored on the eastern side of the plant building,
but by mid-1971, these drums had been moved to the northwest
storage area.
Disposal of Hazardous Waste at NEPACCO
Initially, the still bottoms residues from the NEPACCO pro-
cess were carried away in transport tanker trucks by Rollins-
Purle to their disposal plant in Louisiana. Later, due to cost
considerations, NEPACCO changed from Rollins-Purle to In-
dependent Petrochemical Corporation (IPC). Michaels was
present during negotiations with IPC over the contract to haul
still bottom residues from the NEPACCO plant and warned the
IPC representatives that the still bottoms were toxic and had to
- be handled and disposed of with care.
In or about July of 1971, defendant Mills approached Ray
concerning the disposal of the 55-gallon drums located in the
storage area northwest of the plant. Méills was not in the
business of waste disposal prior to this-date. Ray discussed the
proposal with Lee. Lee defined the desirable disposal site
characteristics, which included soil with a flint or clay consisten-
cy. There was credible evidence that Lee knew and approved of
g
:
3
|
— <n
the proposed use of Mill’s services and the disposal site. Ray
personally went to the disposal site prior to the actual delivery
and reported to Lee on his observations. Mills had previously
contacted James Denney (Denney) and arranged to dispose of
the drums on his farm. The Denney farm site is located approx-
imately seven miles south of Verona, Missouri.
In mid-July 1971, defendant Mills and Gerald Lechner
(Lechner), an assistant hired by Mills, loaded approximately
eighty-five 55-gallon drums containing wastes, located at the
northwest storage site. Defendant Mills and Lechner took the
drums to the Denney farm and deposited them in a large trench
approximately six to eight feet deep, ten feet wide and fifty feet
long. Mills hired Leon Vaughn (Vaughn) to excavate and close
the trench. Within two days, six loads were taken to the Denney
farm site, whereupon, the trench was closed by Vaughn. No
other materials were placed in the Denney farm trench other
than those transported by Mills and Lechner from the Verona
NEPACCO plant. Millis received $150.00 from NEPACCO for
each load that was taken to the Denney farm site and Denney
received $25.00 from Mills for each load.
Mills and Lechner testified concerning the description of the
drums hauled and their contents. According to Mills, most of
the drums were a black metal type with lids. Mills did not recall
whether there were any bung type drums hauled. Mills further
testified that some of the barrels contained a brown liquid
substance and some contained a white substance. Mills was cer-
tain that some of the barrels contained Toluene. Lechner gave a
more detailed description of the barreis and their contents. Ac-
cording to Lechner, some of the drums were a bung type top
and others had the open lid type top. Although most of the
drums were black, some were rust colored. The drums were in a
deteriorated condition. While Lechner was loading the barrels,
he managed to step through the lid of one barrel causing some
of the ‘‘dark sludge’, presumably still bottoms, contained in
the drum to get on his pants leg and boot. Lechner did not
— A-58 —
notice any immediate results but later noted that the substance
‘fate up’’ his pants leg and boot. Lechner testified that he has
suffered no physical injuries from the mishap.
Neither Mills nor Lechner could remember whether they
hauled any drums other than those colored black. James Den-
ney testified that when the trench was opened in 1980 by the
EPA he observed some green drums being taken from the
trench. Denney further testified that within a short period of
time after the trench had been covered, a strong odor emitted
from the trench. This strong odor continued for several mon-
ths, maybe years, but had ceased by 1979.
Gevernmental Response
In October of 1979 the Environmental Protection Agency
(EPA) received an anonymous tip indicating that waste
materials from thé NEPACCO plant had been disposed at the
Denney farm. Under the supervision of Daniel Harris (Harris),
an EPA environmental! engineer and field investigator, the EPA
commenced an investigation. The EPA confirmed through
state records that the NEPACCO operation did generate hazar-
dous waste. In October of 1979, EPA representatives met with
Denney, who confirmed that drums of wastes from the
NEPACCO plant had been buried in a trench at the Denney
farm and identified the location of the trench. EPA represen-
tatives contacted Dr. J. Hadley Williams (Williams), a geologist
with the Missouri Department of Natural Resources, for the
purpose of determining if the Denney farm was suitable for the
disposal of hazardous wastes. Dr. Williams indicated it was
not, due to the nature of the region’s subsurface composition
and ground water conditions. EPA representatives interviewed
approximately 25 other persons in October of 1979 in order to
gain some familiarity with the NEPACCO operation, its wastes,
and its waste disposal practices.
Between January and April of 1980, the EPA, along with
comments from state and federal officials, drafted a plan for an
nuieteieniimacnuaidamall
{
i
2
— A-59 —
on-site investigation at the Denney farm site. Prior to conduc-
ting On-site sampling tests, certain preliminary steps were com-
pleted, which included clearing the disposal site and an access
road and constructing a security fence around the site.
In April of 1980, the EPA commenced the on-site investiga-
tion which consisted of different teams of individuals collecting
soi! samples from boreholes at different distances around the
perimeter of the site, removing a portion of the soil covering the
trench, exposing 13 drums, sampling eight of them, and sampl-
ing the soil in and near the trench. Samples were also taken of
nearby well water. The drums exposed and those finally remov-
ed were in a deteriorated condition, exhibiting extreme rust and
decomposition.
A composite sample from the buried drums, collected during
the April 1980 investigation, was analyzed by Brehem
Laboratories at Wright State University and found to contain a
dioxin concentration as high as 319 parts per million (ppm). Dr.
Michael L. Taylor, associate director of the laboratory, testified
that he immediately telephoned the Region 7 office of the EPA
when he learned of the alarming high concentration of dioxin
found in the composite sample. Other samples from the buried
drums and soil samples collected during the April 1980 in-
vestigation were analyzed by the EPA and found to contain
TCP and toluene in concentrations as high as 6 ppm and 40
ppm, respectively. Dr. Robert D. Kloepfer (Kloepfer), an
analytical chemist and Chief of the Organic Analysis Section for
Region 7, EPA, noted seven samples with concentrations above
1.0 ppm, specifically those concentrations were reported as
follows: drum sample 1—6.6 ppm, drum sample 3—1.1 ppm,
sample No.’s ANO216—1.1 ppm, ANO217—2.1 ppm,
ANO237—6.3 ppm, ANO241—5.6 ppm and ANO271—.9
ppm. The standard variation (degree of accuracy) for these tests
is 25%, higher or lower. The EPA’s principal concern at this
time was the presence of dioxin.
— A-6 — :
After confirming that dioxin was present in the trench and
consulting with Dr. Williams, the EPA in June or July of 1980
installed a temporary cap over the trenc}i to prevent entry of
surface waters into the trench and thereby minimize release of
materials from the trench into the environment. EPA represen-
tatives continued to conduct surface and well water samplings to
monitor the site in order to detect any escape of the materials
from the trench.
Ecology and Environment, Inc. (Ecology and Environment),
under contract with the EPA, prepared an engineering feasibili-
ty study to serve as the plan for further response actions at the
Denney farm site. James Buchanon, regional project manager
for Ecology and Environment, testified that Ecology and En-
vironment was assigned three principal tasks: conduct a
feasibility study, provide expert technical advice at the site and
monitor the site. As part of these tasks, additional on-site
testing was completed to better define the extent of the release
and the size of the disposal trench. The final report and sugges-
tions for remedial action were issued in September, 1980. The
final report and suggestions issued by Ecology and Environment
were made under the hypothesis that the Denney farm trench
contained 26.4 Ibs. of dioxin, the maximum risk potential for
“this site. 7
In July and August of 1980, EPA representatives negotiated
with Syntex concerning the initial cleanup process and respon-
sibilities. On September 3, i980, a consent decree was entered
into by the EPA and Syntex.? In November of 1980, defendant
Syntex proposed a plan for a permanent solution involving the
removal, storage and ultimate disposal of the wastes discovered
at the Denney farm site. Once the Syntex plan was approved by
the EPA, Syntex began excavation of the contents of the
disposal trench in June of 1981. The excavation process took
approximately six weeks, due mainly to the safety precautions
taken against dioxin contamination of the workers.
Se ee Ne
— A-61 —
During the Syntex excavation, numerous drum and soil
samples were collected by the EPA and Syntex. The Syntex
analysis indicated migration of the dioxin into the subsurface
strata of the trench at least as far as 30 inches, in concentrations
ranging from 8.2 parts per billion (ppb) to 532 ppb. While
Syntex is in the process of implementing a permanent solution,
the EPA continues to monitor its implementation of the Syntex
plan and otherwise to meaitor the site and the surrounding area
to detect any past or present movement of hazardous waste
from the site or any significant change in the conditions.
The site was closed in November of 1981 and the drums are
stored in a concrete bunker on the site. According to Harris the
stored hazardous waste no longer presnets an imminent and
substantial endangerment to health or the environment, but
necessitates future monitoring and further response costs.
Endangerment to Health and the Environment
To date, dioxin has produced teratogenic, mutagenic,
fetotoxic and carcinogenic results in low dose levels in various
laboratory animals. Dr. D. Diane Courtney, a pharmacologist
with the EPA, testified that dioxin is particularly devastating to
specific organs of laboratory animals and human beings; ¢.g.,
liver, kidneys, intestines, nervous system, reproductive, and
skin. Dioxin is persistent in the environment and is bio-
accumulative in the tissues of plants and animals. According to
Dr. Courtney, there is presently no known safe level of dioxin in
the environment. Toluene has been shown to cause damage to
the liver and kidneys. Hexachlorophene has known tox-
icological properties and has caused pathological damage,
specifically brain deterioration in newborn animals, as well as
kidney and liver damage. Dioxin, hexachlorophene and toluene
have high levels of toxicity at low-dose levels.
There was a substantial likelihood that the environment and
human beings would be exposed to the toxic wastes dumped in
— A-62 —
the Denney farm trench. Dr. Williams testified that the Denney
farm is located in an area of karst terrain underlain by limestone
bedrock with sinks, underground streams and caverns. The
geohydrology at the Denney farm is such that particles, water
and leachate may move rapidly down through the soil to the
water table below. This rapid movement occurs through ran-
domly occurring discreet openings in the soil and rock. The
ground water beneath the Denney farm was estimated by Dr.
Williams to be the source of water for a number of nearby
residential and agricultural wells. While the ground water
beneath the site is believed to form a water table that may flow
towards Calton Creek, approximately one-third mile from the
Denney farm site, actual rates and directions of ground water
movement in the Denney farm area are impossible to predict.
Unfortunately, it is impossible to predict whether high levels of
toxic dioxin or other hazardous contaminants remain in the
karst soil beneath the Denney farm, presenting future
possibilities of exposure, if the permeability of the soil and
bedrock allow the substances to flow toward the Calton Creek.
Though not conclusive of the ground water movement beneath
the Denney farm site, Dr. Williams did conduct dye tests in the
region. Dr. Wiiliams placed a dye in certain boreholes upstream
on the Calton Creek in the Denney farm region in April of 1980.
One month later, May of 1980, Dr. Williams found traces of
this dye in area springs and wells and collecting in charcoal
packets placed downstream on the Calton Creek. Because of
the region’s soil conditions, there was a substantial likelihood of
the hazardous wastes in the trench at the Denney farm site
entering the environment and going into the ground water
system; whereupon, the contaminants may have come into con-
tact with members of the public who may have been adversely
affected by their exposure to these wastes.
Pursuant to the consent decree, entered September , 1980,
Syntex removed the deteriorated drums and other contaminated
materials from the trench and placed them in temporary
Sona? Settabs shaicr Po ithte Airc scrote Saint asain aeiaieal,
a i le Poe
= Af —
storage, concrete bunker, on the Denney farm site. As of yet,
Syntex has not successfully developed a feasible method of per-
manent disposal. The wastes no longer present an imminent
and substantial endangerment.
DISCUSSION
I. Section 7003 of the Resource Conservation and
Recovery Act of 1976 (RCRA), 42 U.S.C. § 6973 (1980)
Count I of plaintiff's amended complaint is based on
section 7003 of RCRA, which states, in pertinent part:
§ 6973. Imminent hazard
(a) Authority of Administrator
Notwithstanding any other provision of this chapter,
upon receipt of evidence that the handling, storage, treat-
ment, transportation or disposal of any solid waste or
hazardous waste may present an imminent and substantial —
endangerment to health or the environment, the Ad-
ministrator may bring suit on behalf of the United States in
the appropriate district court to immediately restrain any
person contributing to such handling, storage, treatment,
transportation or disposal to stop such handling, storage,
treatment, transportation or disposal or to take such other
action as may be necessary. The Administrator shall pro-
vide notice to the affected state of any such suit. The Ad-
ministrator may also, after notice to the affecte state, take
other action under this section including, but not limited
to, issuing such orders as may be necessary to protect
public health and the environment.
In order to recover the costs expended by the government under
section 7003, the plaintiff must show that the defendants are
such persons contributing to the handling, storage, treatment,
transportation or disposal of a hazardous waste which may pre-
sent an imminent and substantial endangerment to health or the
environment.
—_-
The Court finds that the defendants are not liable under sec-
tion 7003 for the response costs incurred prior to December 11,
1980. The pivotal issue relative to the application of section
7003 to the named defendants is whether the defendants were
**contributing to such handling, storage, treatment, transporta-
tion or disposal’’ within the intended scope of section 7003. It
must first be observed that the plaintiff does not allege
negligence on the part of the defendants. The Court has review-
ed the initial complaint, the amended complaint, the standard
pretrial order No. 2, and trial notes and has found no allegation
of negligence by the defendants. The issue is therefore more
properly narrowed to state, whether a past non-negligent off-
site generator and transporter can be held liable under section
7003 for response costs. Plaintiff contends that the defendants
are ‘‘contributing to’’ the present ‘‘disposal’’ of the hazardous
waste insofar as the hazardous wastes are presently ‘‘leaking”’
from the Denney farm site into the environment. In support of
this proposition, plaintiff further contends that section 7003
does not require present active human involvement but merely a
present imminent and substantial endangerment for which the
defendant is strictly liable, regardless of the time at which the
active human involvement ceased.’ Defendants in opposition
contend that section 7003 does not apply to inactive or aban-
doned sites such as the Denney farm site, United States v. Waste
Industries, 556 F.Supp. 1301, 1303-14 (E.D. N.C. 1982), and
even if section 7003 does apply to inactive sites, section 7003
does not make past non-negligent off-site generators or
transporters liable. United States v. Wade, 546 F.Supp. 785
(E.D. Pa. 1982). After a thorough review and analysis of the
statutory language, case law and legislative history, the Court
finds that section 7003 does not apply to past non-negligent off-
site generators or transporters. Because the Court makes this
narrow finding, it will not be necessary to address the issue of
whether section 7003 applies to inactive or abandoned sites
under different factual circumstances.
— pe
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—_—
If the statutory language is clear and unambiguous, then the
language is controlling. Touche Ross v. Redington, 442 U.S.
560, 568 (1979) and Ernst & Ernst v. Hochfelder, 425 U.S. 185,
197 (1976). If the defendants are to be held liable under section
7003 then they must be classified as part of the class of persons
**contributing to such handling, storage, treatment, transporta-
tion or disposal’’ resulting in the imminent and substantial en-
dangerment. 42 U.S.C. § 6973. Initially, the Court notes that
the phrase ‘‘contributing to’’ is not defined in the statutory
framework of RCRA, specifically 42 U.S.C. § 9603, nor does
the statutory framework of RCRA lend substantial support to
the inclusion of past non-negligent off-site generators or
transporters.
Not having found the statutory framework of RCRA par-
ticularly illuminating on the phrase ‘‘contributing to,’’ this
Court concurs in the language found in City of Philadelphia v.
Stepan Chemical Co., 544 F.Sup. 1135 (E.D. Pa. 1982),
quoting: ‘‘Chief Justice Marshali’s timeless observation that
‘[w]here the mind labors to discover the design of the
legislature, it seizes everything from which aid can be
derived....’ United States v. Fisher, 6 U.S. (2 Cranch) 358,
386 (1805).’’ Jd. at 1142. As numerous courts have noted, the
legislative history of RCRA and specifically 7003 is ‘‘quite sket-
chy,’’ Untied States v. Midwest Solvent Recovery, Inc., 484
F.Supp. 133, 143 (N.D. Ind. 1980), confusing and in some in-
stances seemingly contradicting. Waste Industries, 556 F.Supp.
at 1311; and Wade, 546 F.Supp. at 791. Apparently, Congress’
major purpose in passing RCRA was to control the manner of
disposing of hazardous wastes as opposed to cleaning up the
results of past disposal. RCRA ha been amply termed ‘‘cradle-
to-grave’’ regulatory legislation, designed to trace the life cycle
of hazardous waste.‘ Congress specifically stated the goal of
RCRA as follows:
The Committee believes that the approach taken by this
legislation eliminates the last remaining loophole in en-
—_—~
vironmental law, that of unregulated land disposal of
discarded materials and hazardous wastes... . This legisla-
tion is necessary if other environmental laws are to be both
cost and environmentally eifective.
H.R. Rep. No. 1491, 94th Cong., 2d Sess. 4, reprinted in [1976]
U.S. Code Cong. & Ad. News 6238, 6241-42. The Committee
Report continues to explain how the government has spent
substantial amounts of money on air and water pollution con-
trol merely to have the waste dumped into or on the ground. /d.
A!*hough it could be argued that Congress was unaware of
the pvublems arising from inactive or abandoned sites, Congress
expressly recited such instances of the damage caused by hazar-
dous waste disposal practices in the legislative history. H.R.
Rep. No. 1491, supra, at 17-24, reprinted in [1976] U.S. Code
Cong. & Ad. News at-6254-6261. It would be more properly
stated that Congress was unaware of the magnitude and expense
of inactive or abandoned sites, as well as the lack of current
means or financially responsible parties to clean up those sites.°
This Court concludes that Congress, knowledgeable of the ex-
istence of hazardous waste problems, chose to principally direct
RCRA’s provisions toward the regulation of the source and not
the results of hazardous waste disposal.°
In reviewing the subsequent legisiative history of RCRA and
CERCLA, it appears that Congress and the American public
became more aware of the magnitude and expense of the pro-
blems associated with inactive sites as the Love Canal and
similar sites came to the forefront.’ Congress appeared more
enlightened of the massive problems arising from inactive sites
when discussing the need for further legislation, ‘‘Since enact-
ment of [RCRA], a major new source of environmental concern
has surfaced: the tragic consequences of improperly, negligent-
ly, and recklessly hazardous waste disposal practices known as
the ‘inactive hazardous waste site problem.’ ... Existing law is
clearly inadequate to deal with this massive problem.’’ H.R.
ee ee ee re Tt -
—
Rep. No. 1016, 96th Cong., 2d Sess. 17-18, reprinted in [1980]
U.S. Code Cong. & Ad. News 6119, 6120.°
The only reference in the legislative history that would lend
support to the position that section 7003 applies to past non-
negligent off-site generators or transporters states, ‘‘a company
that generates hazardous waste would be someone ‘contributing
to’ an endangerment under § 7003, even where someone else
deposited the waste in an improper disposal site similar to strict
liability under common law.’’ Report on Hazardous Waste
Disposal by the Subcommittee on Oversight and Investigations
of the House Committee on Interstate and Foreign Commerce,
96th Cong., Ist Sess. 31 (Comm. Print 1979) [hereinafter cited
as Eckhardt Report]. This subcommittee report is subject to
numerous objections.* Most importantly, the broad language
of the Eckhardt Report was not adopted in the full Senate
report which reinstated a standard of negligence under section
7003, in stating:
[Slection 7003 should not be construed solely with respect
to the common law. Some terms and concepts, such as
person ‘contributing to’ disposal resulting in a substantial
endangerment, are meant to be more liberal than their
common law conterparts. For example, a company that
generated hazardous waste might be someone ‘con-
tributing to’ air endangerment under section 7003 even
where someone else deposited the waste in an improper
disposal site (similar to strict liability under common law),
where the generator had «nowledge of the illicit disposal or
failed to exercise due care in selecting or instructing the en-
tity actually conducting the disposal.
S. Rep. No. 172, 96th Cong., 2d Sess. 5, reprinted in [1980]
U.S. Code Cong. & Ad. News 5019, 5023 (emphasis added). At
best, this language would suggest strict liability of present
responsible landowners, but the qualifying phrase ‘‘illicit
disposal or failed to exercise due care’’ requires a finding of
negligence prior to holding past off-site generators or
— Ae —
transporters liable. Although this Court is in agreement that the
phrase ‘‘contributing to’’ is to be given a broad interpretation,
United States v. Price, 523 F.Supp. 1055, 1073 (D. N.J. 1981),
the Court believes the language found in Midwest Solvent
Recovery, Inc., 484 F.Supp. at 144, to be a more prudent con-
clusion, ‘‘Any provision that could logically be read so to ex-
pand the set of persons liable under the federal solid and hazar-
dous waste regulatory scheme would surely be identified as such
in the legislative history.’’ Jd. Accord Waste Industries, 556
F.Supp. at 1308; and Wade, 546 F.Supp. at 790.'°
After a careful review of what this Court believes to be all
cases relevant to the imposition of liability under section 7003,''
it has been unable to find any case in which liability has been im-
posed on past non-negligent off-site generators or transporters.
The broadest scope of liability given the phrase ‘‘contributing
to’’ was in United States v. Price, 523 F.Supp. 1055 (D. N.J.
1981), aff'd, 688 F.2d 204 (3rd Cir. 1982) (denying petition for
preliminary injunction and motion for summary judgment) and
United States v. Price, No. 80-4104 (D. N.J. July 28, 1983) (de-
nying past off-site generators’ motion for summary judgment).
In Price, 523 F.Supp. at 1069-1074, the Court held that liability
under section 7003 could encompass the present owners of the
inactive site, the past principle owner/operator and co-owner of
the site, as well as, an employee of the past owner/operator.
This Court does not deem it necessary to comment at this time
upon the rationale of the district court in Price, 523 F.Supp.,
except to point out that in its subsequent memorandum opi-
nion, Price, No. 80-4104, the court specifically reserved any
decision on the liability of past non-negligent off-site generators
under section 7003. /d., slip op. at 26 n.12.'?
The Court having reviewed the statutory language, the
legislative history and the past judicial interpretations of sec-
tions 7003 concludes that the defendants are not liable under
section 7003. This finding is based upon the Court’s conclusion
that section 7003 does not impose liability upon past non-
negligent off-site generators or transporters.'?
sib ————
— A-69 —
Il. Sections 104, 106(a) and 107(a) of the Comprehensive
Environmental Response, Compensation, and Liability
Act (CERCLA) of 1980, 42 U.S.C. §§ 9604, 9606(a) and
9607(a)
Counts II and III of the amended complaint were brought
pursuant to section 106(a) of CERCLA, 42 U.S.C. § 9606(a)
and sections 104, 107(a) of CERCLA, 42 U.S.C. §§ 9604 and
9607(a), respectively. Specifically, the prayer for relief includes
a request to abate an imminent and substantial endangerment to
health and the environment caused by the continuing storage
and disposal of hazardous waste at the zaney farm site and for
reimbursement of response costs incurred by the plaintiff.
Before dealing with the issues, a brief history and general
outline of CERCLA appears advisable for benefit of further
discussion. CERCLA was enacted in response to the inade-
quacies of RCRA and ‘‘to the growing problem caused by the
large number of uncontrolled ‘inactive hazardous waste sites.’
In fact, Congress, describing the background and necessity for
CERCLA, specifically noted that ‘existing law is clearly inade-
quate to deal with this massive problem. . .{and therefore] the
need for a strong legislative response is evident.’ [citation omit-
ted].”’ Price, No. 80-4104, slip op. at 11. See also Wade, 546
F.Supp. at 792-93. Most importantly, CERCLA establishes two
funding mechanisms for the cleanup and monitoring of hazar-
dous waste sites: the Hazardous Substance Response Trust
Fund, sections 211, 221, 42 U.S.C. §§ 9621 and 9631; and the
Post-Closure Liability Fund, sections 107(k), 111G) and 232, 42
U.S.C. §§ 9607(k), 9611(j) and 9641. After noting the specific
inagequacies of RCRA, Congress stated, ‘‘It is the intent of the
Committee in [CERCLA] ... to initiate and establish a com-
prehensive response and financing mechanism to abate and con-
trol the vast problems associated with abandoned and inactive
hazardous waste disposal sites.’” H.R. Rep. No. 1016, supra, at
22, reprinted in [1980] U.S. Code Cong. & Ad. News at 6125.
See Price, No. 80-4104, slip op. at 12. Suffice it to say in sum-
— A-70 —
mary, section 102 [42 U.S.C. § 9602] requires the government to
promulgate a list of hazardous substances, section 103 [42
U.S.C. § 9603] requires that the release from vessels and
facilities of wastes be reported to the EPA, section 104 [42
U.S.C. § 9604] grants the federal authorities'* broad authority
to respond to hazardous waste pollution by cleaning up the
source and mitigating its effects, section 106 [42 U.S.C. § 9606]
is an imminent hazard provision similar to RCRA’s section 7003
[42 U.S.C. § 6973], and section 107 [42 U.S.C. § 9607] lists
those responsible for the hazardous waste releases as well as
what they are responsible for.'*
A. Retroactive 4 zplication of CERCLA to Non-negligext
Past Off-Site Generators and Transporters
Defendants contend that sections 104, 106(a) and 107(a), 42
U.S.C. §§ 9604, 9606(a) and 9607(a), are not to be given
retroactive application, and if applied retroactively, the statutes
are in violation of constitutional due process. The Court finds
the defendants’ arguments without merit.
It is a well settled rule of law that legislation is presumed to
apply prospectively and that it is the plaintiff’s burden of proof
to show that the statute is to be given retroactive effect. Greene
v. United States, 376 U.S. 149, 160 (1964) (“‘unequivocal and in-
flexible import of the terms, and the manifest intention of the
legislature.’’ Jd.); and Alyeska Pipeline Service Co. v. United
States, 624 F.2d 1005, 1013 (Ct. Cl. 1980). The Court agrees
that the appropriate definition of retroactive application is,
‘‘one which ‘...creates a new obligation, imposes a new duty,
or attaches a new disability, in respect to transactions or con-
siderations already past....’’’ State ex rel. Brown v.
Georgeoff, 562 F.Supp. 1300, 1303 (N.D. Ohio 1983), quoting
Justice Story in Society for Propagating the Gospel v. Wheeler,
22 F.Cas. 756, 767 (C.C.D. N.H. 1814) (No. 13,156).
There can be littie doubt that sections 104 and 107(a) were in-
tended to apply retroactively. A brief review of the case law and
ih
legislative history clearly supports this proposition. It was the
precise inadequacies resulting from RCRA’s lack of applicabili-
ty to inactive and abandoned hazardous waste disposal sites that
prompted the passage of CERCLA. This Court concludes that
sections 104 and 107(a) of CERCLA were intended to apply
retroactively. Georgeoff, 562 F.Supp. at 1302-12; Waste In-
dustries, 556 F.Supp. at 1316-17; Wade, 546 F.Supp. at 792-93;
and Stepan Chemical Co., 544 F.Supp. at 1140-41.
A more perplexing issue is the application of section 106(a) to
inactive or abandoned hazardous waste disposal sites. Section
106(a) is similar to section 7003 of RCRA in that they are both
emergency provisions, but this Court notes several critical dif-
ferences. Section 106(a) authorizes judicial action when an im-
minent and substantial endangerment to the public health,
welfare or the environment is caused by an actual or threatened
release of hazardous waste. Although the statutory language
does not explicitly refer to inactive sites, Congress made this ex-
plicitly clear.'* The Court finds that section 106(a) applies to in-
active sites and that the same persons listed as liable under sec-
tion 107(a) are liable under section 106(a). United States v. Reil-
ly Tar & Chemical Corp., 546 F.Supp. 1100, 1112-13 (D. Minn.
1982); and United States v. Outboard Marine Corp., 556
F.Supp. 54, 56 (N.D. Ill. 1982). To read sections 104, 106(a)
and 107(a) otherwise would be to emasculate the purpose of
CERCLA and the intent of Congress. H.R. Rep. No. 1016,
supra, at 17, reprinted in [1980] U.S. Code Cong. & Ad. News
6119."’
The defendants argue that if CERCLA is applied retroactive-
ly then it violates the Fifth Amendment Due Process Clause.
The fact that a statute has retroactive application does not make
it unconstitutional. Once it has been determined that Congress
intended the statute to apply retroactively, the statute is presum-
ed constitutional.
It is by now well established that legislative acts adjusting
the burdens and benefits of economic life come to the
— + o
Court with a presumption of constitutionality, and that the
burden is on one complaining of a due process violation to
establish that the legislature has acted in an arbitrary and
irrational way.
Usery v. Turner Elkhorn Mining Co., 428 U.S. 1, 15 (1976) (em-
phasis added). The defendants must therefore prove that Con-
gress acted arbitrarily and irrationally in the passage of
CERCLA.
In Turner Elkhorn Mining Co. the defendants challenged the
constitutionality of a provision in Title IV of the Federal Coal
Mine Health and Safety Act of 1969, as amended by the Black
Ling Benefits Act of 1972, 30 U.S.C. §§ 901 et seg. (1970 ed. &
Supp. IV), requiring the payment of benefits with respect to
miners who left employment in the indus'ry before the effective
date of the Act. The Court held the statute constitutional
because Congress acted in a rational manner in formulating the
provisions. /d. at 18. Indeed, “legislation readjusting rights
and burdens is not unlawful solely because it upsets otherwise
settled expectations [citations omitted]. This is true even
though the effect of the legislation is to impose a new duty or
liability based on past acts [citations omitted].’’ Jd. at 16.
It is clear that Congress intended to have the chemical in-
dustry, past and present, pay for the costs of Cleaning up inac-
tive hazardous waste sites. 126 Cong. Rec. $14,962, $14,963
(daily ed. Nov. 24, 1980) (remarks of Sen. Randolph); id. at
$14,966 (remarks of Sen. Stafford); id. at $14,972 (remarks of
Sen. Tsongas); and 12 Cong. Rec. HIl,799 (daily ed. Dec. a
1980) (remarks of Rep. Jeffords). Congress rationally con-
sidered the imposition of liability for the effects of past disposal
practices as a means to spread the costs of the cleanup on those
who created and profited from the waste disposal-generators,
transporters, and disposal site owners/operators. See also
Georgeoff, 562 F.Supp. at 1312; and S.Rep.No. 848, 96th
Cong., 2d Sess. 12 and 33-34, reprinted in [1980] U.S. Code
a MS
Cong. & Ad. News 6119. Accordingly, as in Turner Elkhorn
Mining Co., CERCLA’s imposition of liability for past acts is
rational and satisfies the Due Process Clause of the Fifth
Amendment.'*
Defendants contend that the provisions of CERCLA were not
intended to apply retroactively to costs incurred prior to the ef-
fective date of CERCLA, December 11, 1980, 42 U.S.C. §
9652(a). The plaintiff rebuts this contention by first arguing
that CERCLA specifically states that those liable under
CERCLA, ‘“‘shall be liable for—(A) ail costs of removal or
remedial action incurred by the United States Government . . .
not inconsistent with the national contingency plan... . 42
U.S.C. § 9607(a); therefore, implying that defendants are liable
for all costs regardless of when incurred. Second, plaintiff sug-
gests that Congress specifically intended CERCLA be given
retroactive effect to costs incurred, since Congress failed to in-
clude a provision limiting such recovery in § 9607(a). Finally,
plaintiff contends that the legislative history supports retroac-
tive application to costs incurred. Although the Court has held
that CERCLA applies to past acts of generators and
transporters, rendering them liable for response costs incurred
in cleaning up inactive hazardous waste sites, the prayer for
response costs incurred prior to CERCLA’s enactment is a
separate and distinct new duty from the obligation of post-
CERCLA liability for past acts.
Axiomatic, if the language of the statute is plain and unam-
biguous, then it controls. Section 302 of CERCLA, 42 U.S.C. §
9652 states, in pertinent part:
(a) Unless otherwise provided, all provisions of this
chapter shall be effective on December 11, 1980.
(c) Any regulation—
(1) respecting financial responsibility,
2) issued pursuant to any provision of law repealed or
superseded by this chapter, and
— A-74 —
(3) in effect on the date immediately preceding the effec-
tive date of this chapter shall be deemed to be a regulation
issued pursuant to the authority of this chapter and shall
remain in full force and effect unless or until superseded by
new regulations issued thereunder.
(d) Nothing in this chapter shall affect or modify in any
way the obligations or liabilites of any person under other
Federal or State law, including common law, with respect
to releases of hazardous substances or other pollutants or
contaminants. ...
Clearly, CERCLA became effective on December 11, 1980 and
does not modify financial responsibilities or duties under prior
laws unless specifically done so by provision. The Court in
Georgeoff previously noted that certain ‘‘provisions of
CERCLA support the view that CERCLA applies to pre-
enactment conduct.”’ 562 F.Supp. at 1311. Those provisions
are sections 104(c)(3), 107(f) and 111(d)(1), 42 U.S.C. §§
9604(c)(3), 9607(f) and 9611(d)(1). The plaintiff argues the
same observations made in Georgeoff, 562 F.Supp. at 1311:
CERCLA authorizes reimbursements from the Superfund
for response costs arising before CERCLA’s enactment,
indicating that at least some of the provisions of CERCLA
apply retroactively. Finally, the § 9607(f) prohibition on
recovery for injuries to natural resources occurring before
CERCLA’s enactment suggests, by implication, that a
similar prohibition does not apply to other response costs.
/d. (emphasis added). This Court, as the court in Georgeoff,
562 F.Supp. at 1311-12, concludes that the statutory language is
not equivocal as to the intent of Congress. The statutory
language ‘“‘all costs . . . incurred. . .’’ 42 U.S.C. § 9607(a), is
susceptible to varying interpretations, either all costs incurred
regardless of when incurred or all costs incurred from the date
of enactment. The national contingency plan makes no provi-
sion for the recovery of pre-CERCLA response costs. 40
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C.F.R. Part 300 (1983). References to time limitations placed in
sections 104(c)(3), 107(f) and 111(d)(1) could equally indicate
that these are the only provisions in which pre-CERCLA costs
may be recoverable. Most importantly, there is no clear and af-
firmative statement in the statute allowing for recovery of pre-
enactment response costs.
The only substantive discussion of the retroactive application
of CERCLA to the costs incurred is concerning the originally
drafted senate version of CERCLA, S.1480, as reported out of
the Senate Committee on Environmental and Public Works,
126 Cong. Rec. S.1480 (daily ed. July 11, 1980). The bill con-
tained an amendment introduced by Senator Dominici which
became section 4(n) of S.1480.'° The Sena © version contained
provisions concerning liability for rem: =. costs, section
4(a)(2), S.1480. Section 4(n) speaks to those liability provisions
under section 4(a)(2). The discussions concerning limits of
liability specifically dealt with section 4(a)(2) and not section
4(a)(1). As noted by plaintiff, the Senate Report accompanying
S.1480 states, ‘Section 4(n) specifies how claims for certain
damages occurring before the date of enactment will be handled
under $.1480. Costs of removal (cleanup and containment) are
not affected by this provision, nor are any damages associated
with continuing releases.”” Committee on Environment and
Public Works, $.1480. S.Rep.No.848, 96th Cong., 2d Sess. 344
(1980). Indeed, the plaintiff quotes Senator Dominici, explain-
ing that the purpose of section 4(n), ‘‘is that those kinds of
daimages become part of causes of action or costs of removal
and, therefore, are not affected by the retroactive limitations.’
Transcript of Senate Committee on Environment and Public
Works Mark-Up of S.1480, 194-195 (June 6, 1980).’’ In conclu-
sion, plaintiff suggests that in the absence of specific limitations
on liability for costs of removal or remedial actions, a party is
liable for such costs regardless of when they are incurred so long
as they are not shown to be inconsistent with the national con-
tingency plan.
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The legislative history is unpersuasive. Sections 4(a)(2) and
4(n) of S.1480 were essentially deleted from the enacted com-
promise bill. The only real reference in CERCLA to special
damages concerns destruction and loss of natural resources.
Section 107(a(C) and 111(d)(1), 42 U.S.C. §§ 9607(a)(C) and
9611(d)(1). As noted previously, CERCLA is not the ultimate
tool intended by its sponsors. In fact, the Original senate pro-
posal, S.1480, was severely compromised by the final enact-
ment.*° The lone statement of Senator Dominici falls short of
establishing that Congress intended to hold possibly hundreds
of past transporters and generators liable for pre-CERCLA
response costs, without limit in time or amount. Of equal im-
portance is the lack of discussion in the House concerning the
retroactive application of CERCLA to pre-enactment response
costs.*' Although the Court is cognizant of Congress’ intent to
hold the past generators and transporters liable for the costs in-
curred in cleaning up the results of inactive hazardous disposal
sites,”? in view of the repeated references to the millions of
dollars the government and others have spent on the cleanup of
inactive hazardous disposal sites prior to CERCLA and other
procedural and substantive inadequacies of pre-CERCLA
statutes, it is difficult to believe that if Congress had intended
to make the defendants liable for pre-CERCLA expenses, it
would not have said so explicitly and clearly in the statutory
language, committee reports or floor debates. Alyeska Pipeline
Service Co. v. United States, 624 F.2d 1003, 1016 (Ct. Cl. 1980).
Although it was possible for Congress to legislate the liability of
past generators and transporters for pre-CERCLA response
costs, they did not, and this Court does not deem it advisable to
engage in judicial legislation concerning a statute of such impor-
tance and controversy. All doubts of retroactive application
must be resolved in favor of the defendants; therefore, the
defendants are not liable for pre-CERCLA response costs.
B. Standard of Liability—Strict Liability
Defendants argue that negligence should be the standard for
liability under CERCLA, sections 104, 106(a) and 107(a);
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whereas, the plaintiff advocates a standard of strict liability.
Defendants are correct in noting that CERCLA does not ex-
plicitly contain a strict liability provision and, more important-
ly, the specific strict liability provision contained in the original
Senate bill was deleted from the statute as enacted. Presently,
section 107(a), after listing the categories of liable persons,
reads, ‘‘shall be liable’’ instead of the stricter Senate proposal
which read ‘‘shall be jointly, strictly, and severally liable.’’
S.1480, 96th Cong., 2d Sess., reprinted in, The Environmental
Emergency Response Act: Hearing Before the Senate Comm.
on Finance on S.1480, 96th Cong., 2d Sess. 5 (1980). See also
38 Cong. Q. Weekly Rep. 3436 (Nov. 29, 1980); and 126 Cong.
Rec. HIl, 787 (daily ed. Dec. 3, 1980) (remarks of Rep. Florio).
This Court finds that section 101(32), 42 U.S.C. § 9601(32) pro-
vides for strict iiability of past non-negligent off-site generators
and transporters, when it states: ‘‘ ‘liable’ or ‘liability’ under
this chapter shall be construed to be the standard of liability
which obtains under [section 311 of the Federal Water Pollution
Control Act (FWPCA) (commonly referred to as ‘‘the Clean
Water Act of 1977°’), 33 U.S.C. § 1321 (1981)).”’ Congress’
reference to § 1321 appears quite logical since the same defenses
to liability found in 42 U.S.C. § 9607(b) are also found in § 1321
as a Strict liability provision. United States v. M/V Big Sam,
681 F.2d 432 (Sth Cir. 1982), on petition for rehearing and sug-
gestions for rehearing en banc, 693 F.2d 451 (Sth Cir. 1982);
United States v. LeBeouf Bros. Towing Co., 621 F.2d 787 (Sth
Cir. 1980), cert. denied, 452 U.S. 906 (1981); Steuart Transpor-
tation Co. v. Allied Towing Corp., 596 F.2d 609 (4th Cir. 1979);
United States v. Tex-Tow, Inc., 589 F.2d 1310 (7th Cir. 1978);
and Burgess v. M/V Tamano, 564 F.2d 964 (Ist Cir. 1977); and
City of Philadelphia v. Stepan Chemical Co., 544 F.Supp. 1135,
1140 n.4 (E.D. Pa. 1982).?? Since this Court has already con-
cluded that section 106(a) applies to past off-site generators and
transporters, as does sections 104 and 107(a), the standard for
liability, strict liability, applies equally to all three sections. The
Court finds the defendants can be liable under the theory of
— A-78 —
‘\
strict liability, pursuant to sections 104, 106(a) and 107(a) of
CERCLA.
C. Joint and Several Liability
Defendants contend, inter alia, that liability of the parties
should be based on the relative fault and causation of the parties
resulting in the imminent and substantial endangerment,
whereas, the plaintiff contends that liability is joint and several.
As noted above the final language of Section 107(a), 42 U.S.C.
§ 9607(a), ‘si ull be liable for’’ differs dramatically from the
stricter standard imposed by Senate proposal S.1480, calling for
joint and several liability. This was part of the hastily drawn
compromise which resulted in the enactment of CERCLA.”
Although explicit reference to joint and several liability was
deleted from the final enactment, this Court finds that joint and
several liability is at least permissible, if not mandated, under
the facts of this case. Senator Jennings Randolph, stated during
the debates on the compromise bill:
We have kept strict liability in the compromise . . . but we
have deleted any reference to joing and several liability,
relying on common law principles to determine when par-
ties should be severaily liable.
It is intended that issues of liability not resolved by this
act, if any, shall be governed by traditional and evolving
principles of common law. An example is joint and several
liability. . . . [T]Jhe liability of joint tortfeasors will be
determined under common or previous statutory law.
126 Cong. Rec. $14,964 (daily ed. Nov. 24, 1980) (emphasis ad-
ded).?* Whether the specific standard is to be found in section
311 of FWPCA, 33 U.S.C. § 1321, as set forth in section 101(32)
of CERCLA, 42 U.S.C. § 9601(32), or the common law of the
states, the Court finds to be an oversight of statutory and
legislative guidance. The congressional statements, as noted
above, could lead to both. Granted this issue may be of pin-
— A-79 —
nacle importance in cases involving numerous generators,
transporters, site owners and a different state’s law; however,
the Court deems it unnecessary to address this issue under the
facts of the case at bar, which involve one generator, one
transporter and one landowner in the State of Missouri. The
Court concludes that the imminent and substantial endanger-
ment posed by the Denney farm site was the act of the defen-
dants working in concert to produce a single indivisible harm
and they are therefore jointly and severally liable for the
response costs incurred by the plaintiff, and for which plaintiff
is entitled to recover. Under this finding, the defendants would
be jointly and severally liable pursuant to the law of Missouri.
Stafford v. Muster, 582 S.W.2d 670, 677 (Mo. en banc 1979).
Section 311 of FWPCA, 33 U.S.C. § 1321, has also been con-
strued to allow joint and several liability. See United States v.
M/V Big Sam, 681 F.2d 432, 438-39 (Sth Cir. 1982), on petition
for rehearing and suggestions for rehearing en banc, 693 F.2d
451 (Sth Cir. 1982); United States v. Hollywood Marine, Inc.,
519 F.Supp. 688, 692 (S.D. Tex. 1981); and United States v.
Bear Marine Services, 509 F.Supp. 710, 718-19 (E.D. La.
1980).?¢
D. Imminent and Substantial Endangerment—Section
106(a), 42 U.S.C. § 9606(a)
Plaintiff bases this action, in part, on section 106(a) of
CERCLA, 42 U.S.C. § 9606(a), which states, in pertinent part:
(a) Maintenance, jurisdiction, etc.
. . when the President determines that there may be an
imminent and substantial endangerment to the public
health or welfare or the environment because of an actual
or threatened release of a hazardous substance from a
facility, he may require the Attorney General of the United
States to secure such relief as may be necessary to abate
such danger or threat, and the district court of the United
States .. . shall have jurisdiction to grant such relief as the
public interest and the equities of the case may require... .
—_- po
The listings of hazardous waste include: 2,4,5-Trichlorophenol
(TCP)-U230; Hexachlorophene-U-132; Toluene-U220; and
1,2,4,5-Tetrachlorobenzene (TCB)- U-207. 40 C.F.R. Part 261
(1980) and 40 C.F.R. Part 300 (1982). The Court finds that
these compounds and 2,3,7,8-tetrachlorodibenzo-p-dioxin
(dioxin or TCDD) are hazardous wastes within the meaning of
42 U.S.C. § 6903(5) and 42 U.S.C. § 9601(14). This finding is
based upon the high toxicity of these compounds at relatively
low dosage levels, as noted in this Court’s initial findings of
fact.
Although the phrase ‘‘imminent and substantial endanger-
ment’’ lacks specific definition in CERCLA, this Court is not
without guidance in its query. Section 106(a) is one of several
imminent hazard provisions included in environmental statutes
by Congress.’’ The standard for the application of section 7003
is a case-by-case assessment of the relationship between the
magnitude of risk and harm arising from the presence of the
hazardous waste.** The Court finds that the plaintiff has met its
burden of proof, the Denney farm site presented an imminent
and substantial endangerment to health and the environment.
The quantities of dioxin and other compounds found at the
Denney farm site were highly toxic at low dosage levels and
given the conditions of the soil and bedrock beneath the site,
there was a substantia! likelihood of human and environmental
exposure.
fl. Liability of the Defendants
Having found that there was a release and a threat of con-
tinued release of hazardous waste from the Denney farm site
that constituted an imminent and substantial endangerment to
health and the environment, the Court will address the issue of
whether the defendants are persons liable under sections 104,
106(a) and 107(a), 42 U.S.C. §§ 9604, 9606(a) and 9607(a). Each
defendant will be dealt with separately.
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Mills
Defendant Mills was an independent contractor who con-
tracted with representatives of NEPACCO to transport the
hazardous waste from their facility to the Denney farm site.
Defendant Mills had previously selected the Denney farm site
and contracted with
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