Court Opinion

ID: 2966769
Source: CourtListenerOpinion
Date Created: 2015-09-22 01:09:00.457487+00
Date Added: 2024-06-11T15:01:55.901635
License: Public Domain

Filed:    December 4, 1997

                    UNITED STATES COURT OF APPEALS

                        FOR THE FOURTH CIRCUIT

                           Nos. 96-2003(L)
                          (CA-92-1879-0-17)

United States of America,

                                              Plaintiff - Appellant,

           versus

Hoechst Celanese Corporation,

                                                 Defendant - Appellee.

                              O R D E R

     The Court amends its opinion filed October 27, 1997, as

follows:
     On page 3, section 2, lines 11-12 -- "Douglas W. David" is

corrected to read "Douglas W. Davi s."

     On page 24, second full paragraph, line 7 -- "HCC's" is

corrected to read "HCC."

                                       For the Court - By Direction

                                          /s/ Patricia S. Connor
                                                      Clerk
PUBLISHED

UNITED STATES COURT OF APPEALS

FOR THE FOURTH CIRCUIT

UNITED STATES OF AMERICA,
Plaintiff-Appellant,

v.

HOECHST CELANESE CORPORATION,
Defendant-Appellee.

CHEMICAL MANUFACTURER'S
ASSOCIATION; CORPORATE
ENVIRONMENTAL ENFORCEMENT
COUNCIL; NATIONAL ASSOCIATION OF
MANUFACTURERS; PHARMACEUTICAL
                                    No. 96-2003
RESEARCH AND MANUFACTURERS OF
AMERICA; COMMONWEALTH OF
VIRGINIA; VIRGINIA DEPARTMENT OF
ENVIRONMENTAL QUALITY; SCIENCE &
ENVIRONMENTAL POLICY PROJECT;
TEXAS INSTITUTE FOR ADVANCEMENT
OF CHEMICAL TECHNOLOGY
INCORPORATED; NATIONAL SOCIETY OF
PROFESSIONAL ENGINEERS; TEXAS
NATURAL RESOURCE CONSERVATION
COMMISSION (TNRCC),
Amici Curiae.
UNITED STATES OF AMERICA,
Plaintiff-Appellee,

v.

HOECHST CELANESE CORPORATION,
Defendant-Appellant.

CHEMICAL MANUFACTURER'S
ASSOCIATION; CORPORATE
ENVIRONMENTAL ENFORCEMENT
COUNCIL; NATIONAL ASSOCIATION OF
MANUFACTURERS; PHARMACEUTICAL
                                                              No. 96-2051
RESEARCH AND MANUFACTURERS OF
AMERICA; COMMONWEALTH OF
VIRGINIA; VIRGINIA DEPARTMENT OF
ENVIRONMENTAL QUALITY; SCIENCE &
ENVIRONMENTAL POLICY PROJECT;
TEXAS INSTITUTE FOR ADVANCEMENT
OF CHEMICAL TECHNOLOGY
INCORPORATED; NATIONAL SOCIETY OF
PROFESSIONAL ENGINEERS; TEXAS
NATURAL RESOURCE CONSERVATION
COMMISSION (TNRCC),
Amici Curiae.

Appeals from the United States District Court
for the District of South Carolina, at Rock Hill.
Joseph F. Anderson, Jr., District Judge.
(CA-92-1879-0-17)

Argued: May 5, 1997

Decided: October 27, 1997

Before NIEMEYER and MOTZ, Circuit Judges, and STAMP,
Chief United States District Judge for the
Northern District of West Virginia, sitting by designation.

_________________________________________________________________

                    2
No. 96-2003 affirmed in part and reversed and remanded in part and
No. 96-2051 affirmed by published opinion. Judge Motz wrote the
opinion, in which Chief Judge Stamp joined. Judge Niemeyer wrote
separately, concurring in part and dissenting in part.

_________________________________________________________________

COUNSEL

ARGUED: David Carlisle Shilton, UNITED STATES DEPART-
MENT OF JUSTICE, Washington, D.C. for Appellant. Andrea Bear
Field, HUNTON & WILLIAMS, Washington, D.C. for Appellee. ON
BRIEF: Peter Coppelman, Acting Assistant Attorney General, Envi-
ronment & Natural Resources Division, John A. Bryson, Paul G.
Wolfteich, UNITED STATES DEPARTMENT OF JUSTICE, Wash-
ington, D.C.; Charles Garlow, Mary Ellen Levine, UNITED STATES
ENVIRONMENTAL PROTECTION AGENCY, Washington, D.C.;
David Savage, UNITED STATES ENVIRONMENTAL PROTEC-
TION AGENCY, Atlanta, Georgia, for Appellant. David F. Geneson,
Lee A. Casey, HUNTON & WILLIAMS, Washington, D.C.; Douglas
W. Davis, John Charles Thomas, Claudia T. Farr, HUNTON & WIL-
LIAMS, Richmond, Virginia, for Appellee. Paul G. Wallach, Wendy
E. Anderson, HALE & DORR, Washington, D.C.; David F. Zoll,
General Counsel, James W. Conrad, Jr., Assistant General Counsel,
CHEMICAL MANUFACTURERS ASSOCIATION, Arlington, Vir-
ginia; Jan S. Amundson, General Counsel, Quentin Riegel, Deputy
General Counsel, NATIONAL ASSOCIATION OF MANUFAC-
TURERS, Washington, D.C.; Russel A. Bantham, General Counsel,
Marjorie E. Powell, Assistant General Counsel, PHARMACEUTI-
CAL RESEARCH AND MANUFACTURERS OF AMERICA,
Washington, D.C. for Amici Curiae Chemical Manufacturers of
America, et al. James S. Gilmore, III, Attorney General of Virginia,
Roger L. Chaffee, Senior Assistant Attorney General, Mary Jo
Leugers, Assistant Attorney General, OFFICE OF THE ATTORNEY
GENERAL, Richmond, Virginia, for Amici Curiae Commonwealth
of Virginia, et al. Scott M. DuBoff, John W. Heiderscheit, III,
WRIGHT & TALISMAN, P.C., Washington, D.C., for Amici Curiae
Science and Environmental Policy Project, et al. Geoffrey S. Connor,
General Counsel, TEXAS NATURAL RESOURCE CONSERVA-
TION COMMISSION, Austin, Texas, for Amicus Curiae Commis-
sion.

                   3
OPINION

DIANA GRIBBON MOTZ, Circuit Judge:

In 1984, pursuant to its authority under the Clean Air Act, the
Environmental Protection Agency (EPA) promulgated regulations
governing fugitive emissions of benzene, a carcinogenic pollutant
posing significant risk to human health. This case involves the proper
interpretation of those regulations, which impose numerous preventa-
tive and reporting requirements on industrial plants emitting benzene,
but exempt plants designed to use less than 1,000 megagrams of ben-
zene a year from these requirements. The issue here is whether a plant
owned by Hoechst Celanese Corporation (HCC) is exempted from the
requirements of the regulations. If not, that plant (one of the largest
sources of fugitive benzene emissions in the United States from 1987
through 1993) indisputably violated the regulations in numerous
respects.

The district court sustained EPA's interpretation of its own regula-
tions, an interpretation that did not exempt the HCC plant. United
States v. Hoechst Celanese Corp., 964 F. Supp. 967, 971-76 (D.S.C.
1996). Nevertheless, because the court concluded that the EPA did
not provide HCC with "fair notice" of EPA's interpretation, the court
declined to find HCC liable for any regulatory violations. Id. at 979-
986. Both EPA and HCC appeal. In most respects, we affirm the
judgment of the district court. That court correctly concluded that
EPA's interpretation of its own regulations is entitled to deference.
The district court also correctly held that EPA did not initially afford
HCC fair notice of that interpretation and so the company cannot be
held liable for violations of the regulations during the period (1984 to
1989) when it lacked fair notice. However, the court erred in conclud-
ing that HCC could rely on a fair notice defense for violations that
occurred after 1989 -- when EPA provided the company with actual
notice of EPA's interpretation of the regulations. Accordingly, we
reverse the judgment of the district court in this single respect and
remand the case for further proceedings consistent with this opinion.

I.

The United States, on behalf of EPA, initiated this action against
HCC for alleged violations of the National Emission Standard for

                    4
Equipment Leaks (Fugitive Emission Sources) of Benzene (NESHAP
or regulations), 40 C.F.R. pt. 61, subpts. A, J, and V (1996), at HCC's
Celriver plant in Rock Hill, South Carolina. The NESHAP provides
controls on the amount of benzene that can be emitted into the atmo-
sphere. EPA propounded these controls because it concluded that they
could substantially "reduce the estimated annual incidence of leuke-
mia" for persons living within 20 kilometers of plants with equipment
that leaked benzene -- roughly twenty to thirty million people.
NESHAP preamble, 49 Fed. Reg. 23, 498, 23,501 (1984). Specifi-
cally, the NESHAP requires industrial plants that are designed to pro-
duce, use, or otherwise have in service benzene to monitor equipment
regularly for leaks, repair leaks promptly, and install equipment that
prevents, captures, or destroys benzene emissions. The regulations
include reporting and recordkeeping requirements and provide that
violations are to be punished by civil penalties.

The regulations, however, exempt "[a]ny equipment in benzene
service that is located at a plant site designed to produce or use less
than 1,000 megagrams of benzene per year." 40 C.F.R. § 61.110(c)(2)
(1996) (emphasis added).1 The exemption reflects EPA's conclusion
that the benefit achieved by regulating small volume users of benzene
does not justify the cost involved. See NESHAP preamble, 49 Fed.
Reg. at 23,510. The question that divides the parties is what does
"use" mean in the exemption.

The EPA defines "use" broadly to mean utilization, employment,
or putting in place; this definition includes but is not limited to "con-
sumption" of benzene, i.e., the overall amount needed to keep pro-
cesses operational. The Celriver plant was designed to utilize benzene
as a "quench" to cool hot ketene gases and as a "reflux agent" to help
separate water and other compounds from acetic anhydride and acetic
acid; after each of these uses the benzene was cooled, purified, and
then recirculated as a "quench" or "reflux agent." Under EPA's defini-
tion of "use," counting each time benzene circulated through pipes
and valves capable of leaking, the Celriver plant was designed to
"use" more than a million megagrams of benzene a year, and was not
exempt from the NESHAP. Indeed, the Celriver plant not only "used"
vast amounts of benzene, it also leaked substantial amounts of the car-
_________________________________________________________________

1 One megagram is equivalent to approximately 2,200 pounds.

                    5
cinogen: as the district court noted, "the Celriver plant ranked in the
top 5% of all plants reporting benzene fugitive emissions in every
year between 1987 and 1993." Hoechst Celanese, 964 F. Supp. at
974.

Nevertheless, HCC claims the Celriver plant was exempt from the
NESHAP. The company asserts that "use" in the exemption has only
a single narrow meaning -- "consumption." Since the Celriver plant
continually recycled benzene, the total quantity it "used," under the
company's theory, never exceeded 1,000 megagrams a year and thus
the plant qualified for the exemption under 40 C.F.R. § 61.110(c)(2).
The company concluded that the exemption was self-executing and
for this reason HCC neither filed reports for the Celriver plant nor
complied with any of the monitoring or other requirements of the reg-
ulations.

Because HCC never applied for an exemption for the Celriver plant
or filed any reports as to its benzene usage, EPA did not become
aware of the possibility of substantial benzene emissions at the Cel-
river plant until 1989. At that time, EPA's Region 4 office, which
exercised enforcement authority over plants located in South Caro-
lina, expressly notified the company in writing that if "benzene is
recycled or reused in any process . . . the total cumulative flow
through the process rather than net benzene consumption or usage" is
to be counted as "use" of benzene for purposes of the regulations.
After further communications between the parties, EPA determined
that the Celriver plant had violated the NESHAP and so initiated this
action.

EPA alleged that HCC, at its Celriver plant, violated NESHAP leak
detection and repair requirements as well as requirements related to
the installation of control devices, reporting, and recordkeeping. EPA
asserted the Celriver plant did not qualify for the exemption and, even
if it did, HCC could not claim this protection because it never applied
to EPA for the exemption. In response, HCC argued that EPA's inter-
pretation of the exemption was erroneous and merited no deference.
Alternatively, HCC contended that if EPA's interpretation were
accepted, HCC should not be held responsible for any violations of
the regulations because it lacked fair notice of that interpretation. On
cross-motions for summary judgment, the district court sustained

                    6
EPA's interpretation of the regulations, but concluded that HCC
lacked fair notice of this interpretation both before and after EPA's
direct contacts with HCC in 1989. The court therefore refused to find
HCC liable for any violations of the regulations.

II.

The Clean Air Act unquestionably provides EPA with broad pow-
ers to promulgate regulations necessary to identify and control haz-
ardous air pollutants. See 42 U.S.C.A. §§ 7401-7671q (West 1995 &
Supp. 1997). HCC makes no claim that the benzene regulations in any
way violate or are contrary to EPA's statutory authority. Cf. Chevron,
U.S.A., Inc. v. NRDC, 467 U.S. 837 (1984) (rejecting appellant's con-
tentions that agency's interpretation conflicts with language and legis-
lative history of statute). Nor does the company assert that either the
Clean Air Act or the NESHAP contravenes any constitutional provi-
sion. Finally, HCC does not contend that EPA's procedures in pro-
mulgating the regulations were flawed. Thus, the initial question
before us is simply whether EPA's interpretation of its own autho-
rized, and properly promulgated, regulations should be accorded def-
erence.

The Supreme Court has continually reaffirmed that an agency's
interpretation of its own regulations is entitled to substantial defer-
ence. See, e.g., Thomas Jefferson Univ. v. Shalala, 512 U.S. 504, 512
(1994) ("We must give substantial deference to an agency's interpre-
tation of its own regulations."); Stinson v. United States, 508 U.S. 36,
45 (1993) ("[P]rovided an agency's interpretation of its own regula-
tions does not violate the Constitution or a federal statute, it must be
given controlling weight unless it is plainly erroneous or inconsistent
with the regulation."). When an agency applies its "regulation to com-
plex or changing circumstances," the Court has explained, this "calls
upon the agency's unique expertise and policymaking prerogatives"
and courts must "presume that the power authoritatively to interpret
its own regulations is a component of the agency's delegated lawmak-
ing powers." Martin v. OSHRC, 499 U.S. 144, 151 (1991).

At least implicitly, HCC acknowledges that generally EPA's inter-
pretation of properly promulgated, statutorily authorized, regulations
is entitled to deference. HCC contends, however, that "[t]his is not a

                    7
deference case." Brief of Appellee at 22. The company asserts that the
plain language of the NESHAP does not permit EPA's interpretation.
It further argues that EPA's interpretation merits no deference
because the agency assertedly did not espouse its present interpreta-
tion when it originally promulgated the regulations, but only "created"
that interpretation "during this litigation."

A.

In resolving this question, we begin with the plain language of the
regulations. The NESHAP itself does not indicate any intent to limit
the meaning of the term "use" to consumption. Indeed, EPA's deci-
sion to give "use" a more expansive treatment than that advocated by
HCC is consistent with the ordinary meaning of "use." See Black's
Law Dictionary 1541 (6th ed. 1990) (defining "use" to include "to
make use of, to employ" as well as "to put into action or service, to
utilize").

Nor is the agency's broad interpretation nonsensical. After all,
recycled benzene is just as likely to create a health threat as new ben-
zene; each time benzene passes through a valve or pipe, it can poten-
tially leak. Regulations designed to reduce the risk posed by this
carcinogen should logically treat new and recycled benzene alike.
Thus, EPA's interpretation of its own regulatory exemption harmo-
nizes with the purpose of the authorizing statute, the Clean Air Act:
"to protect and enhance the quality of the Nation's air resources so as
to promote the public health and welfare and the productive capacity
of its population." 42 U.S.C.A. § 7401(b)(1) (West 1995). Congress
mandated that EPA set emission standards that promote the public
health and welfare with "the maximum degree in reduction in emis-
sions of the hazardous air pollutants" subject to the Act, including
cancer-causing benzene. 42 U.S.C.A. § 7412(d)(2) (West 1995). A
broad reading of "use" certainly best achieves this goal.

Moreover, EPA's interpretation of its exemption accords with the
purpose of the exemption itself. As the preamble to the regulations
notes, the exemption was designed as a "small plant exemption"
intended to exclude "most research facilities, pilot plants, and inter-
mittent users of benzene." 49 Fed. Reg. at 23,510. EPA drafted the
exemption in response to comments that the proposed NESHAP

                    8
(which contained no exemption) was not cost effective for small
plants, explaining:

        EPA believes it is reasonable to exempt plants from the
        standard when the cost of the standard is unreasonably high
        in comparison to the achieved emission reductions. There-
        fore, EPA decided to determine a cutoff for exempting these
        plants based on a cost and emission reduction analysis.

Office of Air Quality, EPA, Pub. No. 450/3-80-032b, Benzene Fugi-
tive Emissions - Background Information for Promulgated Standards
2-104 (1982) (BID).

The agency recognized that industrial plants with the fewest pieces
of equipment, and so the fewest sources of leaks, were probably the
least likely to emit emissions. But it determined that it could not
define the exemption in terms of number of pieces of equipment or
sources of leaks because such an approach "could not be applied read-
ily to small or intermittent users of benzene" whose "facilities often
require frequent repiping." BID at 2-104. Instead, EPA conducted
studies and found that when the design production of a plant was
about 1,000 megagrams per year, the plant contained 87 pieces of
equipment and would be expected to emit only about 6 megagrams
of benzene per year; applying the proposed regulations to such plants
would only result in a reduction of 4 megagrams of benzene emis-
sions per year. EPA concluded that the cost of imposing the regula-
tory requirements to such small plants was "unreasonably high in
comparison to the achieved emission reductions" and so those plants
could properly be exempted from the regulatory requirement. Id.
(emphasis added).2

Accordingly, in formulating the exemption, EPA used the 1,000
Mg cut off rate as a proxy to exempt plants that had so few sources
_________________________________________________________________

2 HCC asserts that this regulatory history only demonstrates that the
purpose of the exemption "was to exempt facilities from implementing
the standards of the benzene NESHAP where the cost would be unrea-
sonably high." Brief of Appellee at 26 (emphasis added). That argument,
of course, overlooks the remainder of the language from the administra-
tive record, which is quoted and emphasized above.

                   9
of leaks that they would be expected to emit only 6 megagrams of
fugitive benzene per year. The Celriver plant most decidedly does not
fall within that category. Rather, it had thousands of sources of ben-
zene leaks (nearly 17,000 as of November 1990) and was one of the
largest sources of benzene emissions in the nation during the period
at issue in this suit, with annual emissions reaching 226 megagrams
(nearly 500,000 pounds). Thus, HCC's Celriver plant was not the
kind of plant that EPA envisioned in creating the exemption.

In sum, EPA's interpretation accords with the plain language of the
NESHAP, as well as the purposes of the Clean Air Act and of the
exemption itself.

B.

Nevertheless, HCC asserts that EPA's interpretation merits no def-
erence because it was one "created" after the fact for this litigation.
HCC principally relies on isolated language in the preamble, BID, and
EPA correspondence.3 This scattered language hardly compels the
company's interpretation of the regulations.
_________________________________________________________________

3 HCC erroneously asserts that "there are over 100 places in the rule-
making record where EPA uses the terms `use' and `consume' inter-
changeably." Brief of Appellee at 8. In fact, there are only a few
occasions in the rulemaking record in which EPA employs "consume" in
lieu of "use" and, as explained in text above, those instances are ambigu-
ous. The additional references on which HCC relies are not contained in
the rulemaking record at all. See 42 U.S.C.A. § 7607 (d)(7)(A) (West
1995) (defining rulemaking "record" for purposes of judicial review); 42
U.S.C.A. § 7412(e)(4) (West 1995) (applying § 7607 standards to emis-
sions standards). Rather, they appear in correspondence with various
EPA regional offices or state environmental agencies after the NESHAP
was promulgated. Many of the references in this correspondence were
authored by plant owners and operators, not EPA or other environmental
agencies; furthermore, the agencies' use of "consume" in lieu of "use"
even in the post-promulgation correspondence is subject to differing
interpretations. See infra n.6.

HCC also refers to its interpretation of use as a "single counting"
approach and denominates EPA's interpretation as a "multiple counting"
approach. Although the district court adopted this nomenclature, it does
not appear anywhere in the NESHAP or in the rulemaking record.
Accordingly, we do not employ it here.

                    10
For example, in the preamble, EPA does occasionally employ the
term "consume" in lieu of "use" in a discussion of the operations of
pharmaceutical companies. See NESHAP preamble, 49 Fed. Reg. at
23,510. However, as the district court explained, this scarcely proves
that EPA limited the meaning of "use" in the regulations to "con-
sume":

        These passages from the [administrative] record . . . do not
        lead inevitably to the conclusion that EPA intended the
        word "use" in the exemption to mean only "consume".

Hoechst Celanese, 964 F. Supp. at 976. (emphasis added). Clearly,
one type of "use" is "consumption;" EPA does not claim to the con-
trary. The agency simply asserts that "use" also includes utilization or
employment. Although the preamble contains evidence that "use"
includes "consumption," it in no way requires the conclusion that
"use" is limited to "consumption."

Similarly, EPA describes the exemption in the rulemaking record
as establishing a cut off for "a plant design usage or throughput rate
of benzene equal to or less than 1,000 Mg/yr per plant" and explains
that "throughput" is "determined by a mass balance during the design
stages of process operation, accumulating all benzene processed in 1
year." BID at 2-105. HCC asserts that "throughput" in this context can
only refer to a "plant's overall net production or consumption . . . not
recirculation rates." But again, the district court recognized that
"`throughput' and `consumption' are not synonymous . . . . `through-
put' can describe, for example, the flow of benzene through equip-
ment like the quench chamber and main still"-- just as EPA asserts.

Finally, numerous EPA letters issued in the summer and fall of
1984, shortly after the initial promulgation of the NESHAP in June
1984, severely undermine HCC's entire post-hoc argument.4 For
_________________________________________________________________

4 Recognizing the impact of these EPA documents, HCC urges (some-
what inconsistently with its claim that EPA's interpretation is an after-
the-fact creation for litigation) that these documents demonstrate EPA's
attempt immediately after promulgation of the NESHAP to narrow the
exemption by broadening the meaning of "use." Brief of Appellee at 15.
To prevail on this argument, HCC would have to have demonstrated that
"use" in the NESHAP necessarily meant only "consume." As noted
above, the district court concluded and we agree that this conclusion is
unwarranted.

                    11
example, on August 20, 1984, EPA answered an inquiry from a Tex-
aco plant manager stating that "use" was to be determined by "the
overall quantity of benzene used in equipment," not "consumption."
On October 5, 1984, EPA told an applicant seeking an exemption,
"the 1000 megagrams per year cut off limit is applicable to total
processing rates rather than net consumption (usage) or net produc-
tion, of all affected equipment at an entire plant site." (emphasis in
original). That same month, EPA informed another exemption appli-
cant that the "1,000 megagrams per year cut off limit is applicable to
total processing rates, rather than net consumption (usage) or net pro-
duction." A few days later, EPA wrote still another applicant that the
"1,000 megagram per year cut off limit is applicable to total
processing rates of all affected equipment at an entire plant site."
(emphasis in original). The next month, EPA informed its regional
offices that "We have determined the cut-off is based on the through-
put or processing rate, rather than consumption." There are a number
of other contemporaneous letters from EPA to the same effect. In
view of this evidence, it is simply impossible to conclude, as HCC
argues, that EPA formulated its broad interpretation of the exemption
as a strategy for litigation initiated in 1992, eight years after the regu-
lation was originally promulgated.

For all of these reasons, we agree with the district court that EPA's
interpretation of its own regulations deserves deference.5

III.

The more difficult question is whether, and if so when, HCC was
afforded fair notice of the EPA's interpretation.
_________________________________________________________________

5 In reaching this conclusion, we give no weight to the 1995 affidavit
of a former EPA employee, Robert Ajax, which was prepared and sub-
mitted on HCC's behalf for this litigation. Like similar affidavits from
individual legislators, it is entitled to no weight as to the meaning of leg-
islation enacted, or in this case a regulation promulgated, eleven years
earlier. See Consumer Prods. Safety Comm'n v. GTE Sylvania, Inc., 447
U.S. 102, 118 n.13 (1980) ("Such history does not bear strong indicia of
reliability . . . because as time passes memories fade and a person's per-
ception of his earlier intention may change.").

                     12
Due process requires that a party must receive fair notice before
being deprived of property. Mullane v. Central Hanover Bank &
Trust Co., 339 U.S. 306, 314 (1950). Moreover, it is well established
in criminal law that no punishment can be imposed without notice.
See, e.g., United States v. National Dairy Prods. Corp., 372 U.S. 29,
32-33 (1963); United States v. Bennett, 984 F.2d 597, 605 (4th Cir.
1993). Although the Supreme Court has not directly addressed the
question, we have concluded that because civil penalties are "quasi-
criminal" in nature, parties subject to such administrative sanctions
are entitled to similar "clear notice." See First American Bank v. Dole,
763 F.2d 644, 651 n.6 (4th Cir. 1985). A "regulation[ ] which allow[s]
monetary penalties against those who violate [it], . . . must give . . .
fair warning of the conduct it prohibits or requires, and it must pro-
vide a reasonably clear standard of culpability to circumscribe the dis-
cretion of the enforcing authority and its agents." Id. (quoting
Diamond Roofing Co. v. OSHRC, 528 F.2d 645, 649 (5th Cir. 1976)
(citation omitted)).

To determine if a party has received fair notice, we must examine
the relevant facts of each case. See Bennett, 984 F.2d at 605. In this
case, that requires separate examination of two time frames: (1) the
period from 1984 (when the exemption was originally promulgated)
to 1989 (when EPA became aware of the operations of the Celriver
plant and directly contacted HCC); and (2) the period after the 1989
contacts between EPA and HCC until 1992 (when HCC finally com-
plied with the regulation). We address each period in turn.

A.

In support of its claim that HCC had fair notice of EPA's broad
interpretation of the regulations from the time they were originally
promulgated in 1984, EPA offers two interrelated arguments.

1.

First, the agency asserts that the plain language of the NESHAP
and the rulemaking record should have put HCC on notice that the
Celriver plant did not qualify for an exemption. For example, EPA
contends that HCC should have known that its Celriver plant with
nearly 17,000 pieces of equipment and substantial benzene emissions

                    13
could not possibly be exempt. In support of this argument, EPA
points out that "use" is a broad term, and that what is at issue here is
an exemption and exemptions are to be narrowly construed. See, e.g.,
Duquesne Light Co. v. EPA, 698 F.2d 456 (D.C. Cir. 1983) (narrowly
construing a Clean Air Act exemption). EPA also notes that the rule-
making record indicates that this was intended to be a "small plant"
exemption designed to accommodate companies with limited use and
emissions of benzene. See NESHAP preamble, 49 Fed. Reg. at
23,510. EPA maintains that if HCC had any doubt on the matter
because of EPA's reference to "consume" in lieu of "use" in some
portions of the rulemaking record, it had an obligation to contact the
agency for clarification. See, e.g., Texas E. Prods. Pipeline Co. v.
OSHRC, 827 F.2d 46, 50 (7th Cir. 1987) (finding fault with compa-
ny's failure to make any inquiry of the administrative agency respon-
sible for the regulations at issue).

EPA's argument is not without force and in another case might
well carry the day. Generally, "ignorance of the law or a mistake of
the law is no defense," Cheek v. United States, 498 U.S. 192, 199
(1991), and a claim of lack of notice "may be overcome in any spe-
cific case where reasonable persons would know that their conduct is
at risk." Maynard v. Cartwright, 486 U.S. 356, 361 (1988). However,
as EPA recognizes, "it is crucial to examine the particular situation of
the defendant, and whether it lacked reasonable notice." Brief of
Appellant at 29 (emphasis in original). Examination of the particular
facts of this case convinces us that, prior to 1989, HCC did not have
fair notice of the EPA's broad interpretation of the term "use."

Although as noted above, nothing in the NESHAP itself or the rule-
making record forecloses EPA's interpretation of the exemption, at
the same time nothing mandates it. Indeed, some of the language in
the preamble (e.g., EPA's references to "consume" in lieu of "use")
supports HCC's narrower interpretation. Moreover, as the district
court noted, just because the Celriver plant was not a small plant with
few emissions, it was not necessarily put on notice that it was subject
to the regulations, given that even under EPA's interpretation of
"use," some plants with many pieces of equipment and significant
emissions theoretically could be exempt. Thus, we cannot hold that

                    14
the regulations, their preamble, or purpose clearly put HCC on notice
that the Celriver plant did not qualify for an exemption.6

We need not determine if, as EPA maintains, the NESHAP and
rulemaking record at least provided HCC with "reason to know that
its exemption claim rested on extremely shaky grounds" and so trig-
gered an obligation to ask for clarification of the meaning of "use."
Brief of Appellant at 31. If HCC did have such an obligation, it ful-
filled it by communicating with the Texas Air Control Board
(TACB), the state agency that EPA had empowered to implement and
enforce the NESHAP in Texas.

The undisputed facts are as follows: in August 1984 (a few months
after promulgation of the NESHAP), HCC sought information from
the TACB as to whether an HCC plant located in Bishop, Texas,
which also recycled benzene, was exempt under 40 C.F.R.
§ 61.110(c)(2). The TACB referred HCC to an August 1984 letter that
EPA's Region 6 office sent to a Texaco facility in Texas that used
recycled benzene. This letter stated that "use is not meant to imply
consumption, but rather is meant to reflect the overall quantity of ben-
zene used in equipment at a facility." This letter does seem, as EPA
maintains, to support EPA's broad definition of "use." Indeed, con-
temporaneous HCC internal communications indicate that HCC itself
so interpreted EPA's response; for example, one HCC official hand
wrote on the Texaco letter "Read it and weep" and another HCC offi-
cial wrote a memo noting "EPA recently advised . . . that `use' of ben-
zene includes recycle." However, the TACB interpreted EPA Region
_________________________________________________________________

6 HCC also contends, and the district court held, that EPA regional
offices assertedly interpreted the exemption inconsistently and that this
provides additional support for the company's claim that EPA failed to
provide it fair notice. See Hoechst Celanese, 964 F. Supp. at 981. Some
of the EPA documents on which HCC relies can be read, as the company
asserts, as providing conflicting interpretations of "use." Most, however,
can at least as easily be read as consistently requiring EPA's broad inter-
pretation whenever that question was raised and/or relevant. But given
our conclusion that EPA failed to provide fair notice to HCC from 1984
to 1989, we need not reach the question of whether these documents con-
stitute a proper additional basis for a grant of summary judgment on that
question.

                    15
6's letter to Texaco as indicating that overall inventory was the deter-
minant factor. Thus, the TACB concluded that the Bishop plant quali-
fied for an exemption because it did not maintain an inventory of
more than 1,000 megagrams of benzene. In December 1984, the
TACB sent a short letter to HCC informing the company that the
Bishop plant was "exempt from the requirements of Section 61.112,"
the section mandating source compliance with the NESHAP.
Although EPA Region 6 received a copy of that letter, it took no
action to rescind or invalidate the exemption. HCC then concluded
that the Celriver plant, which used benzene in a manner similar to the
Bishop plant, was also exempt.

In addition to the Bishop plant, HCC operated another plant in
Pampa, Texas. That plant, like the Celriver and Bishop plants, contin-
ually recycled benzene through a closed loop system but because the
Pampa plant "consumed" more than 1,000 megagrams of benzene per
year even under HCC's interpretation of "use," it was not exempt
from the NESHAP requirements. For this reason, in September 1984,
HCC applied to the TACB for a two-year waiver from compliance
with the NESHAP for the Pampa plant so that HCC could "reduce the
quantity of benzene consumed in the plant to less than 1,000 mega-
grams" and thus become exempt. In April 1985, the TACB approved
the waiver request; copies of that request and TACB's approval were
sent to EPA Region 6, which took no action to invalidate the waiver.

These undisputed facts demonstrate that, although HCC made no
direct inquiry as to the application of the exemption to the Celriver
plant, it did not fail to make any inquiry as to the meaning of the
NESHAP. Cf. Texas E. Prods., 827 F.2d at 50. Rather, it asked TACB
for an exemption and waiver of the regulation for two HCC plants
located in Texas, which recycled benzene just as the Celriver plant
did. In response, TACB issued the requested exemption and waiver,
with copies to EPA's Region 6. We recognize that although Region
6 received copies of TACB's letters granting the exemption and
waiver to the Bishop and Pampa plants respectively, those letters
were short and may not have fully informed the agency of their
impact. But in addressing whether a party has received fair notice, we
look at the facts as they appear to the party entitled to the notice, not
to the agency. On the basis of the TACB's actions and the inaction
of EPA Region 6, the company had reason to believe that its interpre-

                    16
tation of the exemption -- equating "use" to"consumption" -- was
accurate. When these facts are viewed in the context of a rulemaking
record that included some references to "use" in lieu of "consume,"
we must conclude that HCC did not receive fair notice of EPA's
broader interpretation of the term in the 1984-89 period.

2.

As a corollary to the above argument, EPA asserts that the
NESHAP required a plant owner to apply for an exemption and file
an initial report and that HCC's failure to do either prevents it from
now claiming a right to the exemption. As noted above, immediately
after EPA issued the NESHAP in 1984, numerous other plant owners
inquired as to the meaning of "use," applied for exemptions, and filed
initial reports. HCC, in contrast, never applied for an exemption or
filed reports.

The district court held that HCC's contacts with TACB constituted
an "indirect[ ]," informal application for an exemption for the Celriver
plant. Hoechst Celanese, 964 F. Supp. at 979. We cannot agree.
Whatever the authority of the TACB or EPA Region 6 in Texas, they
had no authority to grant an exemption in South Carolina and no abil-
ity to grant an exemption (by implication) to a plant about which they
knew nothing. Thus, if the NESHAP had clearly mandated that the
owner of a plant seeking an exemption apply for the exemption,
HCC's Celriver plant failed to meet this requirement.

Accordingly, we turn again to the relevant regulatory language.
The NESHAP provides in pertinent part:

        Any equipment in benzene service that is located at a plant
        site designed to produce or use less than 1,000 megagrams
        of benzene per year is exempt from the requirements of
        § 61.112.

§ 61.110(c)(2) (emphasis added). Thus, the plain language of the reg-
ulation suggests that the exemption is self-executing and provides no
discretion to the EPA administrator to determine whether or not to
grant an exemption. Section 61.110(c)(1) does state that "[i]f an

                    17
owner or operator applies for one of the exemptions in this para-
graph," he must maintain certain records. (emphasis added). But it is
impossible to conclude that this reference clearly requires a plant
owner or operator to file an application for an exemption, in view of
the absence of any explicit directive in § 61.110(c)(2), or any instruc-
tions in any other portion of the regulations as to how, where, when,
or in what form such applications for exemptions are to be made. We
note that elsewhere in the same regulations when EPA requires an
application for a waiver of the NESHAP's requirements, it specifies
in detail the procedures for the application. See 40 C.F.R. §§ 61.10(b),
61.11 (1996); see also § 61.112(c) (1996) (setting out procedures for
application for an alternative method for attaining compliance). Thus,
we do not believe the NESHAP provides fair notice that a plant owner
or operator must apply for an exemption.

Nor do we believe the regulations provide fair notice that the
owner of exempt equipment must file an initial report. The NESHAP
requires an "owner or operator of [an] existing source" of benzene
emissions to file an initial report within 90 days of promulgation of
the regulations. 40 C.F.R. § 61.10(a) (1996). EPA asserts that the
exemption in § 61.110(c)(2) does not allow an owner or operator to
avoid the initial report requirement because that exemption only
exempts "equipment," i.e., "sources," and does not eliminate reporting
obligations imposed in other portions of the NESHAP on owners and
operators of such equipment. EPA may be correct that this is what is
intended. But we cannot hold that the plain language of § 61.10(a)
provides clear notice of this intent. As EPA concedes, the reporting
requirement is linked to the exemption provision; by requiring exempt
companies to file reports, EPA can determine continued eligibility for
that exemption. Since we have determined that HCC lacked fair
notice of the need to apply for an exemption, we can not now hold
it should have known to submit reports to monitor continued eligibil-
ity for an exemption.

In sum, we agree with the district court that prior to 1989, HCC did
not have fair notice of EPA's interpretation of the NESHAP or of a
regulatory obligation to apply for an exemption or file reports.

B.

Finally, we must determine whether HCC continued to lack fair
notice after 1989, when EPA's Region 4 office, the office responsible

                    18
for enforcement of the NESHAP in South Carolina, directly informed
officials at HCC's Celriver, South Carolina plant of the proper inter-
pretation of the regulations.

1.

On June 13, 1989, EPA Region 4 wrote the HCC official responsi-
ble for regulatory compliance at the Celriver plant, informing him that
"[i]f benzene is recycled" then "use" for purposes of the exemption
must be calculated on the basis "of total cumulative flow through the
process rather than net benzene consumption or usage." The EPA let-
ter stated that "it appears that [HCC] may be subject" to the NESHAP
requirements and asked HCC to forward information necessary "to
determine the full extent and duration of all benzene emissions"
within thirty days. Two weeks later, on June 26, HCC responded.
Asserting that the Celriver plant recycled benzene and so under
HCC's definition of "use," i.e., consumption, the plant was exempt,
the company did not forward the requested information.

However, on July 28, 1989, senior HCC Celriver officials met to
discuss the EPA's June 13 letter. Minutes of that July meeting indi-
cate that by that time, HCC officials well understood that EPA did not
accept the company's interpretation of "use." The minutes of the July
meeting note in pertinent part:

        The EPA standard for fugitive benzene emissions may be
        applied to Celriver. The limit of 1000 megagrams benzene
        per year (2,205,000 pounds per year) is applied to through-
        put instead of consumption. Process throughput or recycle
        is considerably greater than this limit. Stringent EPA con-
        trols would thus apply to existing process equipment. The
        full implication of this interpretation must be determined
        and steps taken to meet compliance.

(emphasis added).

Moreover, unaware of HCC's internal discussions of the matter, on
August 18, 1989, EPA Region 4 responded to HCC's June 26 letter
noting that "it appears that you are unaware of EPA's interpretation

                    19
of benzene usage as the term is used to determine applicability." In
this letter, EPA proceeded to explain carefully and in no uncertain
terms that benzene usage equaled "total cumulative flow through
equipment in benzene service rather than net consumption." The letter
contained an explicit example of how to determine usage in the
exemption and asked HCC to forward the information originally
requested in mid-June within thirty days. In September, still noting its
objection to EPA's interpretation, HCC finally forwarded the
requested information -- pursuant to EPA's interpretation of "use,"
the Celriver plant's use of benzene exceeded 2.5 million megagrams
of benzene per year. On February 20, 1990, EPA Region 4 issued
HCC Celriver a notice of violation and in April 1990, HCC submitted
a plan to redesign its Celriver plant to bring it into compliance with
the NESHAP.

In short, HCC received in June 1989 a letter from EPA Region 4
unequivocally setting forth the agency's interpretation, and the record
establishes that at least by July 1989 HCC well understood EPA's
position. Moreover, in August 1989 EPA Region 4 expressly reiter-
ated the interpretation stated in its June letter. Further, these 1989 let-
ters from EPA Region 4 to HCC Celriver must be regarded as
representing the agency's authorative interpretation of the benzene
exemption as it affected the Celriver plant. In its appellate brief, HCC
itself concedes as much. See Brief of Appellee at 45 n.29 ("HCC does
not dispute the fact that EPA Region IV is authorized to communicate
the agency's interpretations of its own regulations to the regulated
community.").

2.

In spite of these uncontroverted facts, the district court held that
HCC "did not have actual notice" of EPA's interpretation "in the sum-
mer of 1989." Hoechst Celanese, 964 F. Supp. at 984. The court rea-
soned that EPA Region 4's 1989 letters to HCC were contrary to
"statements" in the rulemaking record (e.g., "consume" in lieu of
"use") and to other letters from EPA and state environmental agencies
interpreting the NESHAP. Id. For this reason, the court concluded
that HCC had a "legitimate basis for believing" that the 1989 letters
from EPA Region 4 -- the region charged with supervision of the
Celriver plant -- did not "speak[ ] for the Administrator" of the EPA.

                     20
Id. The district court further held that even the notice of violation
could "not be deemed as having provided Hoechst Celanese an
authoritative interpretation of the benzene exemption." Id.

With regard to the asserted conflict between EPA Region 4's 1989
letters to HCC Celriver and statements in the rulemaking record, the
district court's conclusion is at odds with its earlier holding deferring
to EPA's interpretation of the NESHAP. The district court initially
held that it should and would defer to EPA's interpretation inter alia
because the rulemaking record did not conflict with that interpreta-
tion. We believe, as explained above, that the district court correctly
analyzed this issue at the outset of its opinion, when it concluded that
"[t]hese passages from the record . . . do not lead inevitably to the
conclusion that EPA intended the word `use' in the exemption to
mean `consume.'" Id. at 976. Accordingly, we necessarily must reject
the argument that statements in Region 4's 1989 letters to HCC con-
flicted with the rulemaking record.

Nor can HCC rely on letters from EPA and state environmental
agencies to other owners or operators about other facilities that alleg-
edly adopt an interpretation of the exemption contrary to that which
EPA directly conveyed to HCC Celriver in 1989. First, no communi-
cation from EPA Region 4 -- the office charged with enforcement of
the NESHAP in South Carolina -- conflicts with Region 4's defini-
tive 1989 letters to HCC Celriver.7

As to the asserted contrary interpretation of "use" by other EPA
offices or state agencies, HCC presents no evidence that the company
knew of any contrary interpretations issued during or after 1989.
Without contemporaneous knowledge of and reliance on these alleg-
edly inconsistent interpretations, HCC had no reason to believe EPA
_________________________________________________________________

7 Thus, HCC's reliance on Region 4's communications with the
Department of Energy's Savannah River Site (SRS) is misplaced. Based
on information SRS initially supplied in 1989, the EPA could not deter-
mine whether the not-yet-built consolidated incineration facility (CIF)
would be exempt. Subsequently, in 1995, upon learning that the CIF
would recirculate benzene in amounts greater than 1,000 mg/yr, EPA
concluded the operation would be subject to the benzene NESHAP.

                     21
Region 4 was providing it with anything other than EPA's definitive
interpretation of the NESHAP.

Finally, the fact that previous letters from state environmental
agencies concerning HCC plants in Texas and Virginia8 assertedly
conflict with Region 4's 1989 letters to HCC Celriver does not in any-
way undermine the force of the latter. Whether a state environmental
agency had previously supplied advice that may appear to conflict
with EPA Region 4's definitive instruction to the Celriver plant in the
summer of 1989 is immaterial. In 1989, EPA Region 4, indisputably
the office responsible for enforcement of the NESHAP in South Caro-
lina, provided the HCC Celriver, South Carolina plant with unequivo-
cal, actual notice as to how the regulation pertained to that plant's
operations, i.e., benzene usage applied to "total cumulative flow
through equipment in benzene service rather than net consumption."
It is well established that "even if the agency has not given notice in
the statutorily prescribed fashion, actual notice will render that deci-
sion harmless." Riverbend Farms, Inc. v. Madigan, 958 F.2d 1479,
1487 n.7 (9th Cir. 1992); Shelton v. Marsh, 902 F.2d 1201, 1206 (6th
Cir. 1990) (same); New York v. Bowen, 811 F.2d 776, 780 (2d Cir.
1987) (same); Small Refiner Lead Phase-down Task Force v. EPA,
705 F.2d 506, 549 (D.C. Cir. 1983) (same) (dicta). See also Maryland
v. Antonelli Creditors' Liquidating Trust, ___ F.3d ___, No. 96-1111,
1997 WL 523681 (4th Cir. Aug. 26, 1997); Greene v. Whirlpool
Corp., 708 F.2d 128, 131 (4th Cir. 1983).

It would be another matter if different officials within EPA Region
4 had issued conflicting interpretive letters to HCC Celriver. But that
is not the case here. The HCC Celriver plant received but one mes-
sage from EPA Region 4 -- recycled benzene must be counted in
determining how much benzene a plant is designed to use. Letters
from the EPA regional office responsible for the State of South Caro-
lina -- regardless of any conflict with previous guidance received by
another HCC plant from an agency with no authority in South Caro-
lina -- placed the HCC Celriver plant on actual notice of EPA's inter-
pretation.
_________________________________________________________________

8 There is little evidence in the record as to the circumstances of the
Virginia exemption. However, there is no evidence that any EPA
regional office approved that exemption.

                    22
For these reasons, we must conclude that EPA Region 4's 1989
communications with HCC Celriver not only should have put the
company officials at the Celriver plant on notice, but did put them on
notice of EPA's interpretation of the NESHAP. Minutes from HCC's
July 28, 1989 meeting convened after receipt of the first EPA letter
supports this conclusion. These minutes unequivocally demonstrate
that HCC officials understood that "[t]he limit of 1,000 megagrams
benzene per year . . . is applied to throughput instead of consump-
tion." Moreover, if HCC had had any remaining doubts after receipt
of EPA's first letter, EPA's second (August 1989) letter would have
eliminated them.

3.

We also reject the district court's alternative grounds for refusing
to find HCC Celriver liable for any violations of the NESHAP after
August 1989. The district court apparently believed that imposition of
liability was inappropriate for two additional reasons: (1) EPA did not
object to the redesign schedule that HCC Celriver submitted in April
1990 to bring the plant in compliance with the NESHAP and the com-
pany made significant expenditures pursuant to that plan to reduce
overall benzene use by August 1992; and (2) if HCC had applied for
a waiver for the Celriver plant, it would likely have received one.
Hoechst Celanese, 964 F. Supp. at 984-85.

At oral argument, HCC conceded, as it had to, that the present liti-
gation solely addresses liability. Congress has directed that a court
should address a "violator's full compliance history and good faith
efforts to comply" not at the liability phase of the litigation but at the
penalty phase. See 42 U.S.C.A. § 7413(e) (West 1995); see also
United States v. B & W Inv. Props., 38 F.3d 362, 368 (7th Cir. 1994)
(applying § 7413(e) criteria in penalty deliberations). Thus, the dis-
trict court erred when it factored in compliance efforts as a reason for
denying liability.

Moreover, nothing in the NESHAP provides that upon receiving a
proposed compliance schedule, EPA is deemed to accept that sched-
ule if the agency does not respond within a certain period of time. Nor
did EPA's lack of response to the proposed compliance schedule pre-
clude it from imposing civil penalties on HCC. The only possible

                     23
legal basis for such a result would be an estoppel of some sort, and
it is well-established that with rare exceptions"equitable estoppel will
not lie against the Government as it lies against private litigants."
OPM v. Richmond, 496 U.S. 414, 419 (1990); see also United States
v. Agubata, 60 F.3d 1081, 1083 (4th Cir. 1995), cert. denied, 116 S.
Ct. 929 (1996).

Finally, HCC cannot rely on the NESHAP waiver provision which
states:

        Based on the information provided in any request . .. the
        Administrator may grant a waiver of compliance with a
        standard for a period not exceeding two years after the
        effective date of the standard.

40 C.F.R. § 61.11(a) (1996) (emphasis added). The regulatory lan-
guage unambiguously provides that the grant of a waiver is within the
EPA Administrator's discretion. EPA might -- or might not -- have
granted the HCC Celriver plant a waiver if the plant had not met
NESHAP's standards within ninety days, but HCC had no right to
expect one. We will therefore not presume here that the company
would have received a waiver.

Officials at the HCC Celriver plant had actual notice of EPA's
interpretation of the NESHAP at least by the time they received
EPA's August 1989 letter. The NESHAP mandates full compliance
from an existing source within ninety days of the standard's effective
date. See 40 C.F.R. § 61.05(c) (1996). Since HCC lacked fair notice
of EPA's interpretation at the time of promulgation of the benzene
NESHAP, the ninety-day period does not commence until HCC
received actual notice of that interpretation in August 1989. By failing
to comply with the NESHAP's requirements within ninety days after
receiving EPA's August 1989 letter, HCC Celriver necessarily vio-
lated the regulations. These violations continued at least until August
1992. We remand the case to the district court for consideration of the
proper penalties, if any, for those violations.

IV.

We affirm the district court's order in all respects, except as to
whether after August 1989, HCC Celriver had notice of EPA's inter-

                    24
pretation of the NESHAP exemption. We hold that by August 1989,
EPA had provided HCC actual notice that the Celriver, South Caro-
lina plant did not qualify for that exemption. We remand the case to
the district court so that it can determine if, and in what amount, pen-
alties should be imposed for the post-August 1989 violations of
HCC's Celriver plant.

                No. 96-2003 - AFFIRMED IN PART AND REVERSED
                            AND REMANDED IN PART

                     No. 96-2051 - AFFIRMED

NIEMEYER, Circuit Judge, concurring in part and dissenting in part:

I concur in Parts I., II., and III.A., but I find that I must dissent
from Part III.B. I believe not only that the regulatory scheme was
ambiguous but also that the EPA interpreted its regulations with con-
siderable ambivalence, denying any person seeking to comply with
them a consistent and clear course to follow. To penalize a company
that, by concession of the majority opinion, was not given fair notice
of any EPA interpretation at least until 1989 and then thereafter chose
to follow one EPA Region's interpretation over another would be, in
my judgment, fundamentally unfair. I have no difficulty with enforc-
ing any consistent and rational EPA interpretation prospectively, but
to impose penalties in the circumstances of this case is tantamount to
punishment on the unfocused whim of a bureaucracy that could not
itself agree on the proper reading of its own regulation.

The Clean Air Act, 42 U.S.C. § 7401 et seq., creates a diverse regu-
latory scheme to lessen air pollution and confers broad power on the
EPA to draft regulations to implement the statute. In 1984, the EPA
published regulations to control the emission standards for equipment
leaks of benzene, requiring industrial plants producing or using ben-
zene to monitor for leaks, to repair leaks, and to install equipment to
capture benzene emissions. The regulations also impose reporting and
record keeping requirements. Violations are subject to civil penalty.
Intending to exempt small volume producers and users of benzene
because of cost concerns, the regulations exempt those plants that are
designed "to produce or use less than 1,000 megagrams of benzene
per year." 40 C.F.R. § 61.110(c)(2) (emphasis added). The issues in

                    25
this case are whether Hoechst Celanese's Celriver (South Carolina)
Plant produces or uses 1,000 megagrams of benzene per year and
whether the EPA's interpretation of "produces or uses" was suffi-
ciently clear to Hoechst Celanese in 1989 so as to justify imposing on
it penalties for not complying with an EPA official's interpretation of
the regulation within 90 days.

Reading the regulation on its face, the words "produces or uses" are
complementary terms designed to provide a basis of measurement for
the amount of benzene manufactured by or employed at a plant. The
amount of benzene that a plant produces would seem to be a straight-
forward calculation measured by the amount of benzene that exits
from a plant's manufacturing process. To measure the amount of ben-
zene that a plant "uses" in a year would appear to require a measure-
ment of the amount of benzene introduced into the manufacturing
process during the course of a year. This natural reading would thus
include in the amount all inventory of benzene in use at a plant during
the entire year plus any amounts consumed by the process. If that
total were less than 1,000 megagrams per year, one would expect that
the plant would be exempt from regulation.

At different times and in different contexts, the EPA has shared in
part my natural reading of the regulation. When the EPA first pub-
lished its regulations, it appears to have assumed that its own regula-
tions were to be read so that "use" means "consumption." This is
reflected in the preamble to the regulation as originally published,
where the EPA stated:

        The possibility that pharmaceutical operations could be
        adversely affected by the standard is very small. This is true
        for several reasons. First, most pharmaceutical plants use
        very little benzene. According to estimates contained in
        Market Input/Output Studies - Benzene Consumption as a
        Solvent (EPA-560/6-77-034, October 1978, p. 41), 1978
        benzene consumption by pharmaceutical manufacturers was
        about 0.72 Gg. No companies consumed more than 1,000
        Mg/yr in 1978. The commenter states that they consumed
        about 325 Mg/yr during 1981. Thus, it is unlikely that phar-
        maceutical operations would be affected by the standard
        because the final standard exempts equipment at plant sites

                    26
        that are designed to produce or use 1,000 Mg/yr or less of
        benzene. Second, Benzene consumption by the pharmaceuti-
        cal industry is declining rapidly. The market input/output
        study just noted estimates that consumption declined from
        2.14 Gg in 1976 to 0.72 Gg in 1978, a decline of about 66
        percent over the 2-year period.

49 Fed. Reg. 23,510 (June 6, 1984) (emphasis added). But when indi-
vidual representatives of the EPA interpreted EPA regulations, they
recognized that if benzene was introduced into a manufacturing pro-
cess and exited it, the "throughput" should be the basis for measure-
ment in determining "use." For example, on October 16, 1984, an
internal memorandum from the EPA Standard Development Branch
to another section provided:

         As you requested, I will articulate our position on the
        1,000 Mg/yr plant site cut-off in the benzene equipment leak
        standard. This cut-off is based on an analysis showing plants
        having few [pieces of] equipment in benzene service should
        not be covered by the standard. This analysis relates the low
        number of [pieces of] equipment to a process rate in Mg/yr.
        This process rate is not based on consumption of benzene
        but rather throughput through the equipment in all process
        units of a plant site. The standard requires owners/operators
        to demonstrate the design capacity for each process unit in
        a plant, and we should sum these capacities and compare
        this sum to the 1,000 Mg/yr.

(Emphasis added). This position was reiterated a month later by the
EPA's Office of Air Quality Planning and Standards which issued a
memorandum to all EPA Regional Air Program Branch Chiefs as fol-
lows:

        The question is whether the cut-off total is based on con-
        sumption or processing rate. We have determined the cut-off
        is based on the throughput or processing rate, rather than
        consumption.

While various persons at the EPA were debating whether "consump-
tion" of benzene or the "throughput" was to be the basis for measure-

                   27
ment, the EPA Regional Director from Region VI took the position
that the benzene used was to be quantified in the same way as any
inventory of a plant normally would be quantified:

         After review of [the regulatory provision], and based on
        our discussion with Headquarters' staff, we differ from you
        [Texaco] in our interpretation of the provision. It is EPA's
        position that the word use is not meant to imply consump-
        tion, but rather is meant to reflect the overall quantity of
        benzene used in equipment at a facility. In determining the
        environmental, health, economic and energy impacts in set-
        ting the benzene standard, estimates were based on the num-
        ber of pieces of equipment utilizing benzene and the
        quantity of benzene in use, rather than on the overall plant
        consumption (conversion) rate of benzene. Therefore, to
        determine if a plant produces or uses greater than 1000
        megagrams per year of benzene, the total quantity of ben-
        zene in use at the facility needs to be considered, not the
        consumption.

(Emphasis in original). Region VI, thus, required the amount of ben-
zene used to be measured by the "total quantity in use" at the facility
- i.e., an inventory measurement. This letter, originally written to Tex-
aco, was provided to Hoechst Celanese by the Texas Air Control
Board in the course of giving Hoechst Celanese an exemption for its
Bishop Plant in Texas, as it was authorized to do under the Act.

The EPA thus had at least three different approaches for measuring
use: (1) the consumption of benzene in a year, (2) the throughput of
benzene through a plant for a year, and (3) the total quantity in use
at the plant.

In June 1989, the EPA Regional Director in Region IV, which
included jurisdiction over Hoechst Celanese's Celriver Plant, wrote
Hoechst Celanese that the Celriver Plant "may be subject" to benzene
regulation and requested data on Celriver's benzene "throughput on
an annual basis." When Hoechst Celanese responded that the Celriver
Plant was exempt because it consumed less than 1,000 megagrams
per year, the Region IV Director sent a letter stating that "it appears
that you are unaware of EPA's interpretation of benzene usage as the

                    28
term is used to determine applicability." The Region IV Director then
explained:

        [B]enzene usage is intended to mean total cumulative flow
        through equipment in benzene service rather than net con-
        sumption[.] [Y]ou reported your benzene usage for the years
        1984 through 1989 in terms of the amount of benzene added
        to maintain the levels in your closed recirculation system.
        Therefore, the paragraph below provides an example of how
        to calculate benzene usage for a hypothetical example. After
        reviewing the example, you should have a better under-
        standing of how the term benzene usage is to be interpreted.

The letter then described how in a closed recirculation system, the
benzene should be measured at a single point so that it is counted
every time it passes a fixed point. The Region IV Director considered
that this form of measurement was an acceptable interpretation of
"throughput."

Up until this point, the EPA as an agency had not addressed how
to measure benzene in a closed recirculation system. While the EPA
Region VI Director applied the regulation to a closed system by
directing the measurement of the "total quantity in use" at the plant,
the Region IV Director was interpreting it as the rate of flow through
a single point in a closed system. Thus, Region IV proposed
recounting the benzene every time it passed the single point. EPA
Region IV did not, however, explain how many measuring points
should be utilized. In a complex recirculation system made up of a
grid of thousands of pieces of equipment, as was involved at the Cel-
river Plant, there are theoretically an unlimited number of measuring
points at each joint and valve. Under this method, virtually any plant
with a closed recirculation system would never qualify for the 1,000-
megagram-per-year usage exemption.

While I agree with the majority that Hoechst Celanese had notice
of the position of the EPA Region IV in August 1989, this notice
should not, against the background of inconsistent EPA interpreta-
tions over time and throughout the different regions, constitute a
definitive agency-wide EPA notice such that penalties could be
imposed for non-compliance with one interpretation. For these rea-

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sons, I firmly believe that the district court properly concluded that
the 1989 Region IV notice should not be considered the "authoritative
interpretation" of the EPA.

I would go yet further and question whether the Region IV Direc-
tor's notice is at all meaningful in view of the ambiguity about his
interpretation.

For the foregoing reasons, I would affirm the district court's find-
ings in their entirety.

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