Opposition Brief — Elias v. United States
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(2) Suprtae Cone US,
JULI5 2082
No. 01-1502
In the Supreme Court of the Bnies Dass |
ALLAN ELIAS, PETITIONER
VU.
UNITED STATES OF AMERICA
ON PETITION FOR A WRIT OF CERTIORARI
TO THE UNITED STATES COURT OF APPEALS
FOR THE NINTH CIRCUIT
BRIEF FOR THE UNITED STATES IN OPPOSITION
THEODORE B. OLSON
Solicitor General
Counsel of Record
THOMAS L. SANSONETTI
Assistant Attorney General
DAVID M. UHLMANN 7
DAVID C. SHILTON
TODDS. KIM
Attorneys
Department of Justice
os Washington, D.C. 20530-0001
(202) 514-2217
QUESTIONS PRESENTED
The Resource Conservation and Recovery Act of
1976 (RCRA), 42 U.S.C. 6901 et seqg., regulates the
transportation, treatment, storage, and disposal of haz-
ardous waste. Petitioner was convicted under RCRA’s
criminal provisions of improperly storing and disposing
of hazardous cyanide-bearing waste that seriously
injured an individual. The questions presented are:
1. Whether the court of appeals correctly rejected
petitioner’s defense that the United States loses its
authority to enforce the criminal provisions of RCRA
once the Environmental Protection Agency (EPA)
authorizes a State to operate a RCRA hazardous waste
program.
2. Whether the court of appeals correctly concluded
that the United States adequately demonstrated that
petitioner stored and disposed of hazardous waste.
3. Whether the court of appeals correctly rejected
petitioner’s defense that the United States had to show
that the waste was hazardous through a particular test
in an EPA guidance manual.
4. Whether, in the face of allegations of jury tam-
pering, the court of appeals correctly placed the burden
on the United States to show that the alleged jury
tampering did not cause prejudice and placed the bur-
den on petitioner to show that, notwithstanding the
absence of prejudice, there existed juror bias.
(1)
TABLE OF CONTENTS
Opinions below
Jurisdiction
Statement
Argument
Conclusion
TABLE OF AUTHORITIES
Cases:
Chevron U.S.A. Inc. v. Natural Res. Def. Council,
Inc., 467 U.S. 837 (1984)
Electric Serv., In re, 1 E.A.D. 947 (EPA Env. App. Bd.
1985)
Harmon Indus., Inc. v. Browner, 191 F.3d 894
(8th Cir. 1999)
Huddleston v. United States, 485 U.S. 681 31 (1988) pedeenia
Irvin v. Dowd, 366 U.S. 717 (1961)
Jackson v. Virginia, 443 U.S. 307 (1979)
Remner v. United States, 347 U.S. 227 (1954) .........cccsssee
Renaud v. Martin Marietta Corp., 972 F.2d 304
(10th Cir. 1992)
United States v. Dee, 912 F.2d 741 (4th Cir. 1990),
cert. denied, 499 U.S. 919 (1991)
United States v. Fiorillo, 186 F.3d 1136 (9th Cir.
1999), cert. denied, 528 U.S. 1142 (2000)
United States v. Flanagan, 126 F. Supp. 2d 1284
(C.D. Cal. 2000)
United States v. Freeman, 30 F.3d 1040 (8th Cir.
1994)
United States v. Hansen, 262 F.3d 1217 (11th Cir.
2001), cert. denied, 122 S. Ct. 2326 (2002)
United States v. Henry, 136 F.3d 12 (1st Cir.
1998)
15
15
Cases—Continued: Page
United States v. Johnson & Towers, Inc., 741 F.2d
662 (3d Cir. 1984), cert. denied, 469 U.S. 1208
(1985) 15
United States v. Kelly, 167 F.3d 1176 (7th Cir.
1999) 15
United States v. Laughlin, 10 F.3d 961 (2d Cir.
1993), cert. denied, 511 U.S. 1071 (1994) 15
United States v. MacDonald & Watson Waste Oil
Co., 933 F.2d 35 (1st Cir. 1991) 10, 13
United States v. Power Eng’g Co., 125 F. Supp. 2d
1050 (D. Colo. 2000), appeal pending, No. 01-1217
(10th Cir. argued Mar. 20, 2002) 17-18
United States v. Sims Bros. Constr., Inc., 277 F.3d
734 (5th Cir. 2001) 10
United States v. Self, 2 F.3d 1071 (10th Cir. 1998) .......... 15
United States v. Weitzenhoff, 35 F.3d 1275 (9th
Cir. 1993), cert. denied, 513 U.S. 1128 (1995) .............s000 23
United States v. Williams, 195 F.3d 823 (6th Cir.
1999) 15
United States Dep’t of Energy v. Ohio, 503 U.S. 607
(1992) 12, 15, 16
United Techs. Corp. v. EPA, 821 F.2d 714 (D.C.
Cir. 1987) 3
Wainwright v. Witt, 469 U.S. 412 (1985) 24
Wyckoff Co. v. EPA, 796 F.2d 1197 (9th Cir. 1986) ......... 13
Statutes and regulations:
Clean Air Act, 42 U.S.C. 7413 13
Clean Water Act, 33 U.S.C. 1251 et seq.
33 U.S.C. 1319(a) 13
33 U.S.C. 1323(a) 16
33 U.S.C. 1342(b) 13
33 U.S.C. 1342() 13
Resource Conservation and Recovery Act of 1976,
42 U.S.C. 6901 et seq.
V
Statutes and regulations—Continued: Page
42 U.S.C. 6902(a)(7) 3
42 U.S.C. 6921 3,8
42 U.S.C. 6921-6939e (Subtit. C) 2,3, 9,14
- 42, U.S.C. 6922 8
42 U.S.C. 6922-6924 (1994 & Supp. V 1999) ............000. 3
42 U.S.C. 6923 9
42 U.S.C. 6924 (1994 & Supp. V 1999) 9
42 U.S.C. 6925 (1994 & Supp. V 1999) 3,9
42 U.S.C. 6925(c) 13
42 U.S.C. 6925(c)(1) 10
42 U.S.C. 6926 3, 9, 14
42 U.S.C. 6926(b) 3, 8, 9,11
42 U.S.C. 6926(d) 10
42 U.S.C. 6926(e) 4
42 U.S.C. 6927(a) 9
42 U.S.C. 6928 4, 12, 13,17
42 U.S.C..6928(a) 9,13
42 U.S.C. 6928(a)(1) 4,13
42 U.S.C. 6928(a)(2) 4,14
42 U.S.C. 6928(a)(3) 4,11
42 U.S.C. 6928(d) 9, 10, 13, 14, 16
42 U.S.C. 6928(d)-(e) 4,19
42 U.S.C. 6928(d)(2) 2,7
42 U.S.C. 6928(d)(3) 14
42 U.S.C. 6928(d)(4) 14
42 U.S.C. 6928(d)(5) 14
42 U.S.C. 6928(e) 3,7
42 U.S.C. 6930 3
Safe Drinking Water Act, 42 U.S.C. 300g-3 13
18 U.S.C. 1001 £7
40 C.F.R.:
Pt. 260:
Section 260.11(a) 22
Section 260.11(a)(11) 22
Section 260.10 19, 21
Section 260.23 22
Regulations—Continued: Page
Pt. 261 3
Section 261.3(a)(2)(i) 19, 22
Section 261.5(a) 20
Section 261.5(b) 20
Section 261.5(g) 20
Section 261.23 19
Section 261.23(a)(5) 19, 20, 21
Pts. 262-266 3
Pt. 270 3
Section 271.1(f) 11
Section 272.651 &
Miscellaneous:
55 Fed. Reg. 50,327-50,401 (1990) 13
H.R. Rep. 1491, 94th Cong., 2d Sess. (1976) 2
In the Supreme Court of the Gnited States
No. 01-1502
ALLAN ELIAS, PETITIONER
Vv.
UNITED STATES OF AMERICA
ON PETITION FOR A WRIT OF CERTIORARI
TO THE UNITED STATES COURT OF APPEALS
FOR THE NINTH CIRCUIT
BRIEF FOR THE UNITED STATES IN OPPOSITION
OPINIONS BELOW
The opinion of the court of appeals (Pet. App. Al-
A37) is reported at 269 F.3d 1003. An accompanying
memorandum decision (Pet. App. A38-A44) is
unreported.
JURISDICTION
The judgment of the court of appeals was entered on
October 23, 2001, and amended on December 21, 2001.
A petition for rehearing was denied on January 4, 2002
(Pet. App. A127). The petition for a writ of certiorari
was filed on April 4, 2002. The jurisdiction of this Court
is invoked under 28 U.S.C. 1254(1).
(1)
2
STATEMENT
Following a jury trial in the United States District
Court for the District of Idaho, petitioner was convicted
on one count of storing or disposing of hazardous waste
without a permit, knowing that his actions placed
others in imminent danger of death or serious bodily
injury, in violation of 42 U.S.C. 6928(e); two counts of
improper disposal of hazardous waste without a permit
in violation of 42 U.S.C. 6928(d)(2); and one count of
making material false statements to government in-
vestigators, in violation of 18 U.S.C. 1001. Petitioner
was sentenced to 204 months’ imprisonment and or-
dered to pay restitution in the amount of $6.3 million.
The court of appeals affirmed the conviction and sen-
tence of imprisonment, but set aside the restitution
order. Pet. App. A1-A35.
1. Congress enacted the Resource Conservation and
Recovery Act of 1976 (RCRA), 42 U.S.C. 6901 et seq., to
address increasingly serious environmental and health
dangers arising from the generation, management, and
disposal of waste. Congress’s overriding concern was
“the effect on the population and the environment of
the disposal of discarded hazardous wastes—those
which by virtue of their composition or longevity are
harmful, toxic or lethal” and “present a clear danger to
the health and safety of the population and to the
quality of the environment.” H.R. Rep. 1491, 94th
Cong., 2d Sess. 3 (1976). Through Subtitle C of RCRA,
42 U.S.C. 6921-6939e, Congress created a nationwide
program for protecting the public from the dangers of
improper hazardous waste disposal. Subtitle C estab-
lishes a “‘cradle-to-grave’ regulatory structure oversee-
ing the safe treatment, storage and disposal of hazard-
3
ous waste.” United Techs. Corp. v. EPA, 821 F.2d 714,
716 (D.C. Cir. 1987).
RCRA charges the Environmental Protection
Agency (EPA) with responsibility to establish a com- —
prehensive national regulatory program for hazardous
waste management. EPA must identify hazardous
wastes, 42 U.S.C. 6921; see 40 C.F.R. Pt. 261, which
triggers notification requirements for facilities engaged
in hazardous waste activity, 42 U.S.C. 6930. EPA must
also prescribe regulatory standards for generators and
transporters of hazardous waste and owners and
operators of hazardous waste treatment, storage, and
disposal facilities. 42 U.S.C. 6922-6924 (1994 & Supp V
1999); see 40 C.F.R. Pts. 262-266. In addition, EPA
must establish a permit program for owners and opera-
tors of such facilities. 42 U.S.C. 6925 (1994 & Supp. V
1999) ; see 40 C.F .R. Pt. 270.
RCRA also creates a process by which a State may
request EPA to “authorize” a state hazardous waste
program to operate “pursuant to this subchapter,”
meaning Subtitle C of RCRA. See 42 U.S.C. 6926 (Pet.
App. A128-A132). (Subtitle C of RCRA is codified as
Subchapter III of Chapter 82 of Title 42 of the United
States Code.) To receive authorization, a state regula-
tory program must be equivalent to and consistent with
the federal program and must provide for adequate
enforcement. 42 U.S.C. 6926(b).
RCRA directs EPA to ensure that hazardous wastes
are managed nationally in a responsible manner.
42 U.S.C. 6902(b). At the same time, it has long been a
federal goal and EPA policy to encourage and support
States that seek authorization for their hazardous
waste management programs. 42 U.S.C. 6902(a)(7).
Recognizing both the national interest in consistent and
effective implementation of the RCRA program and the
4
state interest in program administration at the local
level, RCRA provides for the co-existence of indepen-
dent federal and state authority in authorized States. |
Thus, while States can assume responsibility for pro-
gram administration at the local level, EPA has con-
tinuing oversight responsibilities concerning the activi-
ties regulated under state programs. For example,
EPA has authority to revoke a state-issued permit if
the permittee fails to comply with RCRA requirements,
42 U.S.C. 6928(a)(3), and to withdraw program authori-
zation if the State is not administering its program in
accordance with RCRA, 42 U.S.C. 6926(e).
RCRA also vests the federal government with inde-
pendent authority to take direct enforcement action in
States with authorized hazardous waste programs.
42 U.S.C. 6928 (Pet. App. A133-A140). For instance,
EPA may issue compliance orders and assess admini-
strative civil penalties against those who violate RCRA
in such States, and it may also request the Justice
Department to commence a judicial action seeking in-
junctive relief and civil penalties. 42 U.S.C. 6928(a)(1).
In either instance, Congress has directed EPA to give
notice to the State before “issuing an order or com-
mencing a civil action under this section.” 42 U.S.C.
6928(a)(2). The United States may also seek federal
criminal penalties against persons who knowingly vio-
late RCRA requirements, including persons who fail to
obtain, or violate the requirements of, “a permit under
this subchapter.” 42 U.S.C. 6928(d)-(e).
2. Petitioner owned Evergreen Resources, a fertil-
izer company located near Soda Springs, Idaho. Pet.
App. A2. In August 1996, petitioner decided to store
sulfuric acid in a 25,000-gallon tank that held at least
one to two tons of cyanide-laced sludge. Ibid. Peti-
tioner knew, based on his prior use of the tank, that the
5
sludge contained cyanide. Ibid.; id. at A38-A39. He
decided that the sludge, which was hardened and more
than a foot deep, had to be disposed of before he could
use the tank for sulfuric acid storage. Id.at A2. __
On August 26, 1996, petitioner ordered four of his
employees, Bryan Smith, Gene Thornock, Darrin
Weaver, and Scott Dominguez, to enter the tank and
wash the sludge out of a valve opening in the end. Pet.
App. A2. Despite Smith’s repeated requests, petitioner
failed to provide any safety equipment. Ibid. Conse-
quently, Dominguez and Weaver entered the tank
wearing only their regular work clothes. Jd. at A2-A3.
After about fifteen minutes, they realized that the
sludge could not be washed out the small valve opening,
and they exited. Jd. at A3. Both complained of sore
throats and nasal passages. Ibid.
The next morning, on August 27, 1996, petitioner met
with his employees, who told him of the difficulties of
the day before and tha health effects they had suffered.
Pet. App. A3. Smith again insisted on the necessary
safety equipment. Ibid. Petitioner said he would pro-
vide safety equipment, but he directed his employees to
commence cleaning the tank without the equipment and
stated that he expected the tank to be cleaned out that
morning. Ibid. On past occasions, petitioner had simi-
larly failed to take adequate safety precautions to
protect employees from cyanide exposure. Id. at A39.
After cutting a bigger drainage opening in the end of
the tank, Dominguez and Weaver again entered the
tank with no safety equipment. Pet. App. A3. About 45
minutes later, after they had emptied about one-third of
the sludge through the hole onto the ground, Weaver
shouted that Dominguez had collapsed. Ibid. Thornock
and Smith unsuccessfully tried to get Dominguez out of
the tank, which had only a 22-inch manhole at the top.
6
Ibid. When firefighters arrived to rescue Dominguez,
he was in severe respiratory distress and in danger of
dying. Ibid.
After extricating Dominguez, the fire chief asked
petitioner whether cyanide might be in the tank. Pet.
App. A3. Petitioner insisted that he had no knowledge
of anything in the tank other than water and sludge,
which the fire chief understood to mean mud. [bid.
After Dominguez was rushed to the hospital, the
treating physician concluded that the most likely cause
of his condition was cyanide poisoning. Id. at A3-A4.
He called petitioner and asked whether the tank might
contain cyanide, to which petitioner again replied no.
Id. at A4. The doctor nonetheless ordered a cyanide
antidote kit, to which Dominguez responded positively.
Ibid. Blood tests showed extremely toxic levels of
cyanide in his body. Ibid.
Dominguez now suffers from permanently debilitat-
ing injuries, including severe neurological impairment.
Pet. App. A81; Tr. 1383-1385, 3226-3228. He exhibits
symptoms like those associated with Parkinson’s dis-
ease, with slow and rigid muscle movements, poor bal-
ance, and a very “flat” demeanor. Tr. 3194, 3199-3201.
He cannot drive or hold a job or care for himself for any
extended periods. Tr. 3268-3273. He has great diffi-
culty feeding himself, and his parents must wake up
several times a night to turn him over in bed. Tr. 3268-
3269. His symptoms are classic results of cyanide
poisoning. Tr. 3199-3200, 3216-3224, 3226-3227, 3523.
The day Dominguez was injured, petitioner told
investigators that he had completed a confined space ©
entry permit, but he declined to show it to them. Pet.
App. A4. Early the next morning, petitioner visited an
acquaintance at a nearby company, where he inquired
about the requirements for confined space entries and
7
departed with a copy of a safety manual that spelled out
the requirements for a confined space entry permit.
Ibid . The permit that petitioner eventually provided to
investigators stated that it was issued on August 27,
1996, at 10:30 a.m. Ibid.
Petitioner had a long history of failures to handle
cyanide and confined space entries properly or to pre-
pare his employees to do so. Pet. App. A38-A39. His
previous failures and attempts to evade enforcement
were exhaustively documented at trial. E.g., Tr. 1938-
1957, 2012-2034, 2074-2075, 2155-2164, 2182-2189, 2273-
2331, 2343-2345, 2551-2562, 2826-2830, 3099-3104, 3182-
3183.
‘8. A federal grand jury returned an indictment
against petitioner. Pet. App. A4, A45. Count I charged
that he had stored or disposed of hazardous waste with-
out a permit, knowing that his actions placed others in
imminent danger of death or serious bodily injury in
violation of 42 U.S.C. 6928(e). Pet. App. A4-A5, A45.
Counts II and III charged petitioner with improper dis-
posal of hazardous waste without a permit in violation
of 42 U.S.C. 6928(d)(2). Pet. App. A5, A45. Count IV
charged him with a violation of 18 U.S.C. 1001 for
making material misstatements relating to the confined
space entry permit that he alleged was prepared on
August 27, 1996. Pet. App. A5, A47. The jury found
petitioner guilty on all four counts. Jd. at A5, A465.
4. The court of appeals affirmed the conviction and
the resulting seventeen-year prison sentence in a pub-
lished opinion and an unpublished memorandum. Pet.
App. Al-A44. Although petitioner raised and the court
ruled on numerous issues, only four are relevant here.
First, the court rejected petitioner’s defense that the
United States lacks authority to enforce the criminal
penalties set out in RCRA in States with authorized
8
hazardous waste programs. Id. at A6-A14. Second, the
court ruled that the United States had to demonstrate
only that some of the sludge was’ hazardous in order to
prove the RCRA counts, and it rejected petitioner’s
assertion that the United States had to examine what
petitioner considered a more “representative sample”
of all the waste from the tank. Jd. at A15-A17. Third,
the court held that the United States was not required
to employ a test for “hazardous” levels of cyanide that
EPA published in a guidance document in 1985 and
that, in any event, that test did not undermine the
conclusion that the waste here was hazardous. Id. at
A21-A24. Fourth, the court affirmed the district court’s
conclusion that a new trial was not required on account
of two jury members’ belief that petitioner’s brief
greeting to another juror had consisted of a joking offer
of a bribe. Jd. at A28-A3z2.
ARGUMENT
1. Petitioner contends (Pet. 9-17) that RCRA does
not grant the United States the authority to bring an
enforcement action for violations of RCRA permitting
requirements in States that are authorized, under
RCRA, to issue state permits for storage and disposal
of hazardous waste. See 42 U.S.C. 6926(b); see also 40
C.F.R. 272.651 (EPA’s authorization of Idaho’s pro-
gram). The court of appeals correctly rejected that
argument, which rests on a fundamental misapprehen-
sion of RCRA and the resulting hazardous waste
regulatory program. See Pet. App. A6-A14.
a. As explained above (pp. 2-4, supra), RCRA
creates a national program for regulation of hazardous
wastes. It directs EPA to set out national standards
identifying hazardous wastes, 42 U.S.C. 6921, and regu-
lating their generation, 42 U.S.C. 6922, transportation,
9
42 U.S.C. 6923, and treatment, storage, and disposal,
42 U.S.C. 6924 (1994 & Supp. V. 1999). RCRA also
creates a national program, administered by EPA, for
issuing permits to persons who own or operate facilities
for treatment, storage, and disposal of hazardous
wastes. 42 U.S.C. 6925 (1994 & Supp. V. 1999). RCRA
additionally provides, however, that individual States
may develop their own hazardous waste programs.
42 U.S.C. 6926. If a State develops a program that is
consistent with RCRA’s requirements, and EPA
“authorizes” the program, then the State program
operates “pursuant to this subchapter” (i.e., Subtitle C
of RCRA). 42 U.S.C. 6926(b).
The fact that EPA has authorized a state hazardous
waste program does not mean that the federal gov-
ernment thereafter lacks authority to enforce RCRA
requirements, including the requirements of the
authorized state program. Rather, RCRA explicitly
preserves that federal authority. See, ¢.g., 42 U.S.C.
6927(a) (preserving EPA’s authority to request infor-
mation from “any person” who stores, treats, trans-
ports, handles, or disposes of hazardous wastes); 42
U.S.C. 6928(a) (preserving EPA’s authority to issue a
compliance order to “any person” who is in violation of
“any requirement of this subchapter”); 42 U.S.C.
6928(d) (subjecting “[a]Jny person” who knowingly vio-
lates RCRA requirements to federal criminal sanc-
tions).
Petitioner’s contrary view rests on a misreading of
the relevant provisions. Petitioner mistakenly suggests
that Section 6926 of RCRA allows States to “opt out of
the federal RCRA program.” Pet. 10; see id. at 14.
Quite the opposite is true. Section 6926 allows States to
opt into RCRA by developing a “hazardous waste pro-
gram pursuant to this subchapter.” 42 U.S.C. 6926(b)
10
(emphasis added). Contrary to petitioner’s suggestion
(Pet. 15-16), the RCRA provisions governing authoriza-
tion of state programs do not require the delegation of
federal authority to States. Hence, petitioner’s sugges-
tion that such a delegation would pose constitutional
problems is without merit.’
Section 6926(d) of RCRA, entitled “Effect of State
permit,” makes clear that, upon EPA’s authorization of
the state program, the State’s permitting actions “have
the same force and effect as action taken by the Ad-
ministrator under this subchapter.” 42 U.S.C. 6926(d).
As a consequence, the federal government may bring
an enforcement action based on state permit violations,
including the failure to obtain a permit. See, ¢.g.,
United States v. MacDonald & Watson Waste Oil Co.,
933 F.2d 35, 44 (1st Cir. 1991). As the First Circuit ex-
plained in the specific context of criminal enforcement:
The statute [Section 6928(d)] criminalizes “Any per-
son” who acts without, or in respect to facilities
lacking, “a permit under this subchapter.” A permit
under this subchapter is one issued by the Admin-
istrator of the EPA or by an authorized state. 42
U.S.C. § 6925.
933 F.2d at 44. See 42 U.S.C. 6925(c)(1) (“Upon a deter-
mination by the Administrator (or a State, if applica-
ble), of compliance by a facility for which a permit is
1 RCRA does not require a State to develop a state hazardous
waste program. If it does develop such a program, the State may
enforce the requirements of its program as a matter of state law,
whether or not the program receives EPA authorization. EPA’s
authorization of a state program pursuant to RCRA is significant
because, among other things, that authorization allows the federal
government to enforce the state permitting requirements under
federal law. 42 U.S.C. 6926(d).
=
11
applied for under this section with the requirements of
this section and section 6924 of this title, the Adminis-
trator (or the State) shall issue a permit for such facili-
ties.”); see also, e.g., 42 U.S.C. 6928(a)(3) (authorizing
EPA to issue orders suspending or revoking “any per-
mit issued by the Administrator or a State under this
subchapter”).
Petitioner also misreads Section 6926(b)’s specific
provisions for authorization of a state program. Pet. 10,
13-14. Those provisions direct that, once a State sub-
mits an application for authorization of a state program,
EPA shall issue a notice of whether it expects to
authorize the program. 42 U.S.C. 6926(b). Section
6926(b) then continues:
Such State is authorized to carry out such program
in lieu of the Federal program under this subchapter
in such State and to issue and enforce permits for
the storage, treatment, or disposal of hazardous
waste * * * unless, witiin ninety days following
submission of the application the Administrator
notifies such State that such program may not be
authorized * * *.
42 U.S.C. 6926(b). That passage, read in context, sim-
ply makes clear that, once a state program is author-
ized, permit applicants should submit their applications
to the State rather than EPA. 42 U.S.C. 6926(b). See
40 C.F .R. 271.1(f) (“upon approval of a State permitting
program, the Administrator shall suspend the issuance
of Federal permits for those activities subject to the
approved State program”). The passage provides no
basis for concluding that the federal government may
not continue to exercise its explicit enforcement powers
under RCRA. See Pet. App. A8-A9. —
12
Contrary to petitioner’s assertion (Pet. 10), this
Court’s decision in United States Department of En-
ergy v. Ohio, 503 U.S. 607 (1992), does not suggest that
Section 6926(b)’s “in lieu of” language deprives the fed-
eral government of enforcement authority. The Court
stated:
RCRA regulates the disposal of hazardous waste in
much the same way [as the Clean Water Act, 33
U.S.C. 1251 et seq.], with a permit program run by
EPA but subject to displacement by an adequate
state counterpart.
Id. at 611 (emphasis added). See Pet. App. A13 n.29.
The Court did not questoin EPA’s power to exercise
enforcement authority in States that have EPA-
authorized water pollution control programs. See 33
U.S.C. 1819(a), 1842(b), 1842(i).?
Petitioner also points to the fact (Pet. 10-11) that
EPA’s regulations for approval of state hazardous
waste programs require States to include “remedies for
violations of State program requirements.” 40 C.F.R.
271.16. But there is nothing unusual in the fact that
both the federal government and the state government
can take enforcement action with respect to the same
wrongs. The concept of dual enforcement is a familiar
2 Petitioner’s reliance on a passage from RCRA’s legislative
history suggesting that a State may “take over the hazardous
waste program” (Pet. 10 n.5 (emphasis added by petitioner)) is
similarly misplaced. That passage plainly is speaking to state
assumption of responsibility for issuance of permits, since RCRA’s
text explicitly preserves federal enforcement authority. See, ¢.g.,
42 U.S.C. 6928 (discussed in text infra). Indeed the more relevant
legislative history, pertaining to Section 6928, indicates that the
federal government retains its criminal enforcement authority. See
Pet. App. All1-A13; MacDonald, 933 F 2d at 44-45.
13
feature of federal environmental law. See, e.g., 33
U.S.C. 1819(a), 1342(b), 13424) (Clean Water Act); 42
U.S.C. 300g-3 (Safe Drinking Water Act); 42 U.S.C.
7413 (Clean Air Act). Indeed, in the preamble to the
Federal Register notice first codifying Idaho’s author-
ized hazardous waste program, EPA emphasized that it
“retains the authority under [42 U.S.C. 6928] of RCRA
to undertake enforcement actions in authorized states.”
Pet. App. A9 n.14 (quoting 55 Fed. Reg. 50,327-50,401
(1990)).
Moreover, RCRA’s specific enforcement provisions
explicitly preserve federal enforcement in States with
authorized programs. Section 6928(a)(1) empowers
EPA to issue a compliance order or seek civil judicial
relief against “any person [who] has violated, or is in
violation of any requirement of this subchapter.”
42 U.S.C. 6928(a)(1). Because RCRA allows EPA or an
authorized State to issue a permit, 42 U.S.C. 6925(c),
the failure to obtain a permit from either is a violation
of a “requirement[] of this subchapter.” See Pet. App.
A8-A10; Wyckoff Co. v. EPA, 796 F.2d 1197, 1199-1200
(9th Cir. 1986). Similarly, Section 6928(d) subjects
“[alny person who * * * knowingly treats, stores, or
disposes of any hazardous waste identified or listed
under this subchapter * * * without a permit under
this subchapter” to federal criminal prosecution. 42
U.S.C. 6928(d). Like Section 6928(a), Section 6928(d)
does not distinguish between federal and state permits.
Thus, Section 6928 preserves the full panoply of federal
enforcement options. Pet. App. Al3 (“the federal gov-
ernment retains both its criminal and its civil enforce-
ment powers”); MacDonald, 933 F.2d at 44 (Section
6928(d) “does not limit prosecutions thereunder to
14
those who deal with facilities lacking a federal
permit..”).3
In short, when EPA authorizes a state prograru, the
program operates “pursuant to” Subtitle C of RCRA
(42 U.S.C. 6926), but that authorization does not disable
the federal government from continuing to exercise its
overarching authority to enforce Subtitle C through
criminal sanctions. Pet. App. Al3. Even if RCRA’s
“plain language and legislative history” were not suffi-
cient to eliminate any doubt on that score, EPA’s long-
standing interpretation of RCRA would be entitled to
deference as a reasonable construction of a regulatory
statute by the agency charged with its administration.
3 As the court of appeals and MacDonald explain, the legis-
lative history of Section 6928(d) confirms the meaning of the text.
Pet. App. All-A13 (quoting MacDonald, 933 F.2d at 44-45). As
they specifically observe:
The 1984 amendments [to Section 6928(d) of RCRA] increased
the applicable criminal penalties and simply substituted “under
this subchapter” for the references to the specific subsections
under which permits, federal and state, may be granted. The
new language, “without a permit under this subchapter,” sub-
sumed both state and federal permits, as both types are
provided for within “this subchapter.” The latter did not,
therefore, in any way narrow the scope of federal criminal
jurisdiction.
Id. at Al2-A13. The text of other portions of Section 6828 also
demonstrates that federal enforcement authority survives state
authorization. For example, Section 6928(a)(2) directs EPA to
notify a State before taking civil enforcement action in a State that
has an authorized program. 42 U.S.C. 6928(a)(2). Additionally,
Section 6928(d) makes specific reference to criminal sanctions for
non-compliance with “regulations promulgated by the Admini-
strator (or by a State in the case of an authorized State program)
under this subchapter.” 42 U.S.C. 6928(d)(3), (4) and (5).
15
Pet. App. A7-A9; see, e.g., Chevron U.S.A. Inc. v. Natu-
ral Res. Def. Council, Inc., 467 U.S. 837 (1984).
b. Petitioner is wrong in his assertions (Pet. 11-12,
14-16) that the court of appeals’ construction of RCRA
conflicts with decisions of this Court or another court of
appeals. Neither this Court nor any court of appeals
has ever held that the United States loses its enforce-
ment powers under RCRA upon authorizing a State
program. To the contrary, the courts of appeals have
repeatedly affirmed federal convictions under RCRA
based on unlawful activities in States with authorized
RCRA programs.‘
There is no merit to petitioner’s contention (Pet. 14-
15) that the court of appeals’ decision in this case
‘conflicts with United States Department of Energy v.
Ohio, 503 U.S. 607 (1992). The Court in that case ruled
that Congress had not waived the federal government’s
sovereign immunity from liability for civil penalties
that a State sought to impose against a federal facility
for alleged past violations of the CWA and RCRA. Id.
at 611. Thus, the issue in that case bears no similarity
* See, e.g., United States v. Henry, 136 F.3d 12 (1st Cir. 1998)
(New Hampshire); United States v. Laughlin, 10 F.3d 961 (2d Cir.
1993) (New York), cert. denied, 511 U.S. 1071 (1994); United States
v. Johnson & Towers, Inc., 741 F.2d 662 (3d Cir. 1984) (New
Jersey), cert. denied, 469 U.S. 1208 (1985); United States v. Dee,
912 F.2d 741 (4th Cir. 1990) (Maryland), cert. denied, 499 U.S. 919
(1991); United States v. Sims Bros. Constr., Inc., 277 F.3d 734 (5th
Cir. 2001) (Louisiana); United States v. Williams, 195 F.3d 823 (6th
Cir. 1999) (Tennessee); United States v. Kelly, 167 F.3d 1176 (7th
Cir. 1999) (Wisconsin); United States v. Freeman, 30 F.3d 1040
(8th Cir. 1994) (Missouri); United States v. Fiorillo, 186 F.3d 1136
(9th Cir. 1999) (California), cert. denied, 528 U.S. 1142 (2000);
United States v. Self, 2 F.3d 1071 (10th Cir. 1993) (Utah); United
States v. Hansen, 262 F.3d 1217 (11th Cir. 2001) (Georgia), cert.
denied, 122 S. Ct. 2326 (2002).
16
to the issue posed here. Petitioner nevertheless focuses
on passages from the decision that rejected Ohio’s
contention that a State’s assessmént of civil penalties
under an EPA-authorized state water pollution control
program is permissible under Section 1323(a) of the
Clean Water Act because those state-law penalties
“aris[e] under Federal law” (33 U.S.C. 1323(a)). See 503
U.S. at 623-627. The Court recognized that “the
complementary relationship between state and federal
law” did not support the State’s argument that “state-
law fines thereby ‘arise under Federal law.’” Id. at 625
(emphasis added). This federal prosecution, however,
does not involve “state-law fines.” The Court in no way
suggested that the federal government’s pursuit of
federal criminal sanctions against an individual pur-
suant to Section 6928(d) of RCRA would be beyond the
federal government’s authority. As the court of appeals
correctly recognized, that issue “was not an issue
presented to or resolved by the Ohio court.” Pet. App.
A13-A14 n.29.
Petitioner is also wrong in asserting (Pet. 11-12) that
the court of appeals’ decision conflicts with Harmon
Industries, Inc. v. Browner, 191 F.3d 894 (8th Cir. 1999)
(reproduced at Pet. App. Al45-A164). That case
involved a federul government practice known as “over-
filing.” The federal government had initiated a civil
enforcement action and continued that action after a
State with an authorized program had resolved a state
enforcement action on terms that the federal govern-
ment believed to be inadequate. See 191 F.3d. at 897-
898 (Pet. App. A150). As the court of appeals explained
in this case, Harmon held that the federal government
may not continue to pursue its own civil penalty action
after a State that has an authorized program has
settled the identical claim with the same defendant.
17
Pet. App. A10-All. See 191 F.3d at 902 (Pet. App.
A159) (“TW]e find that the EPA’s practice of overfiling,
in those states where it has authorized the state to act,
oversteps the federal agency’s authority under the
RCRA.”). But that court did not rule that EPA lacks
authority to bring its own enforcement action in the
absence of a state enforcement proceeding. See id. at
901 (Pet. App. A158) (EPA may proceed in accordance
with Section 6928 “when the authorized state fails to
initiate any enforcement action.”); see also id. at 902 n.4
(Pet. App. A158 n.4) (reconciling its decision with
Wyckoff on that basis).
As the court of appeals correctly recognized, Har-
mon “is not about if, but about when, the United States
can bring a civil enforcement action in federal court
after it has authorized a state program.” Pet. App. All
(quoting United States v. Flanagan, 126 F. Supp. 2d
1284, 1289 & n.3 (C.D. Cal. 2000)). Because the decision
in Harmon dealt with an instance of the federal
government’s “overfiling” during a state civil action,
and that decision expressly recognized that a federal
enforcement action is permissible where, as here, there
has been no state enforcement action, Harmon does not
conflict with the decision in this case. (Indeed, in this
case, the State of Idaho expressed its concurrence with
the United States’s criminal enforcement action. Govt.
C.A. Supp. E.R. 58-59.) Hence, even assuming that
Harmon is correct, that decision “does not support
[petitioner’s] contention that federal law is supplanted
or that the United States lacks power to try him.” Pet.
App. All.
5 The United States District Court for the District of Colorado
has declined to follow Harmon, concluding that it “incorrectly
interprets the RCRA.” United States v. Power E'ng’g Co., 125 F.
18
Petitioner is also mistaken in asserting (Pet. 12-13)
that the decision of the court of appeals conflicts with
Dague v. City of Burlington, 935 F.2d 1343 (2d Cir.
1991), rev’d in part, 505 U.S. 557 (1992). Contrary to
what petitioner argues, that decision does not hold that
the phrase “pursuant to this chapter” in RCRA’s
*itizen-suit provision, 42 U.S.C. 6972(a)(1)(A), excludes
suits alleging violations of permitting programs in
authorized States. Indeed, that provision was not even
at issue. The plaintiffs there had raised a claim under
42 U.S.C. 6972(a)(1)(A) but had not appealed its
dismissal. 935 F.2d at 1348-1349, 1352. As relevant
here, the decision in Dague states in dictum that “an
EPA-authorized state hazardous waste program * * *
can supersede the permit and notification requirements
of [Subtitle C].” Jd. at 1852. The decision does not bar
citizens from bringing suit under RCRA to enforce
permitting requirements in authorized States and does
not address federal enforcement authority at all.
2. Petitioner contends (Pet. 17-22) that the court of
appeals erred in failing to require the United States to
show that the waste in question was hazardous based
on what petitioner considered a more “representative
sample” of the waste from the tank. Contrary to peti-
tioner’s arguments, the court of appeals correctly rec-
ognized that the government was under no obligation to
test all of the cyanide-containing wastes in the tank and
that there was ample evidence from which the jury
could conclude that the waste was hazardous. Pet. App.
A15-A17. That fact-specific decision is correct and does
Supp. 2d 1050, 1059 (2000). That decision is currently on appeal to
the United States Court of Appeals for the Tenth Circuit. No. 01-
1217 (10th Cir. argued Mar. 20, 2002).
19
not conflict with any decision of this Court or another
court of appeals.
To obtain convictions on the counts of the indictment
under RCRA, the United States was required to prove
that petitioner stored or disposed of hazardous waste
without a permit. 42 U.S.C. 6928(d)-(e). EPA has de-
fined “hazardous waste” by regulation to include solid
wastes that have the characteristic of reactivity. 40
C.F.R. 261.3(a)(2)(i), 261.23 (Pet. App. A142-A143).
Cyanide-bearing wastes are reactive, and thus hazard-
ous, if a “representative sample” shows that the waste
is capable of generating “toxic gases, vapors or fumes in
a quantity sufficient to present a danger to human
health or the environment.” 40 C.F.R. 261.23(a)(5). A
sample is “representative” if it “can be expected to ex-
hibit the average properties of the universe or whole.”
40 C.F.R. 260.10 (Pet. App. A141). In this case, a
sample is sufficiently representative if it exhibits the
average properties of the wastes that were removed
from the tank, since those wastes were sufficient, by
themselves, to establish storage and disposal violations.
See Pet. App. A16-A17 (citing In re Electric Serv. Co., 1
E.A.D. 947 (EPA Env. App. Bd. 1985)).
As the court of appeals explained, the United States
did not need to show that all the waste in the tank was
hazardous; rather, the government fulfilled its burden
at trial by proving that petitioner had improperly
stored or disposed of some hazardous waste. Pet. App.
Al6. Because (1) the waste samples that the United
States’ experts examined tested positive for cyanide,
(2) the samples included waste that petitioner’s em-
ployee was forced to remove from the tank, and (8) that
employee became incapacitated and permanently in-
jured through cyanide poisoning, the samples were
sufficient to support the convictions. Jbid. As the court
20
of appeals observed, “[i]f a sample from one part of the
tank contains wastes reactive enough to cause brain
damage to someone, there can be no conceivable
purpose in sending other people into the tank to extract
more samples.” Jd. at Al7.° -
Petitioner’s “hypertechnical interpretation” not only
defies “common sense” (Pet. App. A17), it ignores the
underlying purpose and import of EPA’s regulations,
which seek to avert the type of injury that occurred in
this case. EPA requires “representative” samples to
ensure that the hazardous characteristics of the mate-
rial in question are properly identified. Jbid.; see Tr.
3324-3327. If a hazardous waste, such as cyanide-
bearing sludge, is discovered in a tank, then “it’s not
necessary to go to every inch of the tank to see if
there’s more cyanide there.” Pet. App. A17. It is suffi-
cient if the sample demonstrates that the waste “can
generate toxic gases, vapors or fumes, in a quantity suf-
ficient to present a danger to human health or the
environment.” 40 C.F.R. 261.23(a)(5).
In any event, “the relevant question is whether, after
viewing the evidence in the light most favorable to the
prosecution any rational trier of fact could have found
the essential elements of the crime beyond a reasonable
§ Petitioner contends (Pet. 19 n.16) that, if he had only stored or
disposed of “the few grams of cyanide-bearing waste tested,” he
would qualify as a small-quantity generator under EPA’s regula-
tions and would be exempt from prosecution. But petitioner was
not prosecuted for those few grams, but for improper storage and
disposal of wastes from which those samples were taken. Pet.
App. A2. The samples were sufficient, together with the other evi-
dence the government produced, to establish that the wastes were
hazardous. Indeed, even if petitioner could have qualified as a
small-quantity generator, he would still be subject to RCRA
requirements. See 40 C.F.R. 261.5(a), (b) and (g).
21
doubt.” Jackson vy. Virginia, 443 U.S. 307, 319 (1979).
The record here includes ample evidence from which a
rational jury could conclude that the samples exhibited
the “average properties” of the waste that was improp-
erly stored and disposed of, including all the waste in
the tank, and that the waste was hazardous. See 40
C.F.R. 260.10 (defining “representative sample”),
261.23(a)(5) (describing the characteristic of reactivity
in the case of cyanide-bearing compounds).
First, the samples that were taken indicated that the
wastes in the tank demonstrated the characteristic of
reactivity. Tr. 3340-3347. Second, an expert explained
at trial how the sampling of the sludge, under the
circumstances, was representative and that there was
no need to put those conducting the sampling at further
risk by having them enter the tank to take more
samples. Tr. 3344-3351, 3429-3434, 3463-3465. Third, a
hazardous materials team that responded to the site
additionally found hydrogen cyanide gas in samples
taken from both inside and outside the tank. Tr. 1108-
1110, 1180-1209. And fourth, petitioner’s injured em-
ployee, who was directly exposed to the wastes in the
tank, demonstrated the symptoms and permanent
effects of cyanide poisoning. Tr. 3223-3228, 3194-3200.
The evidence adduced at trial, viewed in its totality,
demonstrated beyond doubt that the waste within the
tank could generate gases sufficient “to present a dan-
ger to human health” and was thus hazardous. 40
C.F.R. 261.23(a)(5). See Huddleston v. United States,
485 U.S. 681, 691 (1988) (“[I]ndividual pieces of evi-
dence, insufficient in themselves to prove a point, may
in cumulation prove it.”). The evidence plainly was
sufficient for the jury to have concluded, beyond a
reasonable doubt, that the waste was hazardous under
22
the regulations. That factbound determination does not
warrant review by this Court.’
3. Petitioner argues (Pet. 22-26) that he lacked fair
notice of the standards under which he could be con-
victed because a sample of the waste was not hazardous
under an EPA guidance manual, known as SW-846, that
elaborated on a test for cyanide-bearing wastes. That
non-binding guidance described a test method for
determining whether cyanide-bearing waste is reactive.
Contrary to petitioner’s suggestion (Pet. 25), the guid-
ance manual is not incorporated into EPA’s regulations
for purposes of determining whether a waste is reac-
tive, and thus hazardous. See 40 C.F.R. 261.3(a)(2)(i),
260.11(a) and (a)(11), 261.28. In any event, his
argument fails for two main reasons.
First, SW-846 did not purport to draw a line between
what was and what was not hazardous waste. Instead,
that guidance suggested a “quantitative threshold for
toxic gas generation” above which waste was clearly
hazardous, without denying that some wastes below
that threshold would also be hazardous. Pet. App. A21-
A22. That is, the guidance did not purport to indicate a
“‘safe harbor’ for waste that emitted toxic gas below
the threshold level.” Id. at A24, A86. Petitioner admit-
ted as much in his reply brief in the court of appeals.
C.A. Rep. Br. 19. Thus, even if the United States were
bound by SW-846, the fact that the waste at issue was
” Petitioner suggests (Pet. 21) that the court of appeals’ deci-
sion is in tension with Renaud v. Martin Marietta Corp., 972 F.2d
304 (10th Cir. 1992), which observed, in the context of a tort claim,
that “no one has any idea whether this [particular] sample is rep-
resentative of the ‘normal’ contaminant concentration.” Id. at 308.
That remark, made outside the RCRA context, plainly does not
give rise to a conflict among the courts of appeals.
23
not proven hazardous under that test would present no
reason to question petitioner’s conviction.
Second, petitioner’s “fair notice” argument founders
on the undisputed fact that petitioner did not even
know of SW-846. Pet. App. A23. Although he argues
that “fair notice” arguments do not depend on actual
notice, Pet. 23-24, his argument is not really based on
“fair notice” at all. Petitioner no longer contends that
the underlying regulation would be impermissibly
vague and that he would lack fair notice without the
quantitative threshold provided by SW-846. The court
of appeals rejected that argument, Pet. App. A17-A20,
and petitioner does not renew it here. Rather, he now
relies on the argument that EPA cannot disclaim SW-
846 because EPA had used it for some purposes in the
past. Pet. 22-23, 25-26. As the district court recog-
nized, that argument rests on estoppel, not fair notice.
Pet. App. A90-A91. Because such an argument is
unavailable absent actual reliance by the party claiming
estoppel, it is unavailable to petitioner here. bid.; see
United States v. Weitzenhoff, 35 F.3d 1275, 1290 (9th
Cir. 1993), cert. denied, 513 U.S. 1128 (1995).
4. Petitioner argues (Pet. 26-28) that the court of
appeals erred by concluding that he bore the burden to
show that he had been prejudiced by two jurors’ belief
that his brief greeting to another juror had consisted of
a joking offer of a bribe. He mistakenly contends that
this allocation of the burden conflicts with decisions of
this Court and various other courts of appeals. Jbid.
Petitioner misapprehends the decision of the court of
appeals. Contrary to his contention (Pet. 27), that court
did not flout this Court’s decision in Remner v. United
States, 347 U.S. 227 (1954), by requiring him to carry
the burden to show that any jury tampering did not
prejudice him. The district court found that no juror
24
thought that he had tampered with the jury and that
the United States had carried its burden of dispelling
any associated presumption of prejudice. Pet. App.
A123. The court of appeals affirmed the district court’s
findings as not clearly erroneous. Jd. at A30-A32.
Thus, the decision is consistent with the decisions that
petitioner cites indicating that jury tampering raises a
presumption of prejudice that the government bears
the burden to dispel.®
The court of appeals referred to petitioner’s burden
in addressing a separate question: whether the jury
was nevertheiess biased against him even though no
juror believed that he actually tampered with the jury.
Pet. App. A382 & n.70. The district court addressed that
issue separately from the “closely related” issue of jury
tampering and noted that the defendant bears the
burden of showing that a juror is biased. Jd. at A1C*,
A123. The district court concluded that petitioner had
not carried the burden of showing any such bias. Jd. at
A123. The court of appeals affirmed, stating that “the
district court’s conclusion that [petitioner] had not
borne his burden of showing juror bias appears
correct.” Jd. at A382 (footnote omitted). That allocation
of the burden of showing bias is consistent with this
Court’s decisions. E.g., Wainwright v. Witt, 469 U.S.
412, 423 (1985); Irvin v. Dowd, 366 U.S. 717, 723 (1961).
Petitioner cites no decisions that question that result.
8 Although petitioner is correct that there is some disagree-
ment among the courts of appeals on whether the government
always bears the burden of showing that jury tampering did not
prejudice the defendant, Pet. 26-27 & n.18, the government carried
that burden here and thus this case does not present an occasion
for resolving the tension in those cases.
25
CONCLUSION
The petition for a writ of certiorari should be denied.
Respectfully submitted.
THEODORE B. OLSON
Solicitor General
THOMAS L. SANSONETTI
Assistant Attorney General
DAVID M. UHLMANN
DAVID C. SHILTON
ToppS. Kim
Attorneys
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