UNITED STATES
ENVIRONMENTAL PROTECTION AGENCY
BEFORE THE ADMINISTRATOR
In the Matter of )
)
H.E.L.P.E.R., Inc. ) Docket No. EPCRA-VIII-95-06
)
Respondent )
INITIAL DECISION
Pursuant to Section 325(c) of the Emergency Planning and
Community Right-to-Know Act ("EPCRA"), 42 U.S.C. §11045(c), the
charges against the Respondent H.E.L.P.E.R., Inc., are dismissed.
Respondent did not have present in its facility the threshold
amounts of hazardous chemicals that would require submittal of a
material safety data sheet and hazardous chemical inventory form as
required by EPCRA §§311 and 312, respectively, 42 U.S.C. §§11021
and 11022.
Appearances
For Complainant:
Brenda L. Morris, Esq.
Assistant Regional Counsel
U.S. EPA Region 8
Denver, Colorado
For Respondent:
T.R. Pardy, Esq.
Mumford, Protsch & Pardy
Madison, South Dakota
Proceedings
The Region 8 Office of the United States Environmental
Protection Agency (the "Complainant" or the "Region") filed an
administrative Complaint, dated May 23, 1995, against H.E.L.P.E.R.,
Inc. (the "Respondent" or "HELPER"). The Complaint charged
Respondent with two violations of the Emergency Planning and
Community Right-to-Know Act ("EPCRA") at Respondent's facility in
Madison, South Dakota.
Count I of the Complaint alleges that Respondent failed to
timely submit a material safety data sheet for the hazardous
chemical polychlorinated biphenyls ("PCBs") to the South Dakota
State Emergency Response Commission ("SERC"), the Local Emergency
Planning Commission ("LEPC"), and the local fire department,
constituting a violation of EPCRA §311, 42 U.S.C. §11021. Count II
of the Complaint alleges that Respondent failed to timely submit a
hazardous chemical inventory form for PCB-contaminated liquids to
the SERC, LEPC, and fire department, constituting a violation of
EPCRA §312, 42 U.S.C. §11022. The Complaint seeks assessment of a
total civil penalty of $20,790 against Respondent for these two
violations. In its Amended Answer, Respondent denied the material
allegations of the Complaint and requested a hearing.
The hearing in this matter convened before Administrative Law
Judge Andrew S. Pearlstein on January 28, 1997, in Sioux Falls,
South Dakota. The Region presented two witnesses, and HELPER
presented five witnesses. The record of the hearing consists of a
stenographic transcript of 262 pages, and 16 numbered exhibits
received into evidence. The parties each submitted post-hearing
briefs and reply briefs. The record of the hearing closed on May
13, 1997, upon the ALJ's receipt of the reply briefs.
Findings of Fact
1. The Respondent, H.E.L.P.E.R., Inc. ("HELPER"), is the owner
and operator of an industrial facility located at Airport
Industrial Park, Old Highway 34, Madison, Lake County, South
Dakota. HELPER is in the business of processing, reconditioning,
and recycling the components of used electrical equipment. HELPER
receives, stores, and manages electrical transformers and
capacitors that contain liquids contaminated with polychlorinated
biphenyls ("PCBs"). (Ex. 9; Tr. 115).
2. HELPER has received EPA approval to operate as a commercial
PCB storage facility, pursuant to Section 7 of the Toxic Substances
Control Act, 15 U.S.C. §2605, and 40 CFR §761.65(d). The approval
authorized HELPER to store a maximum of 8000 gallons of mineral oil
dielectric fluid ("MODEF") containing from 50 to 499 parts per
million ("ppm") of PCBs; 3000 pounds of PCB capacitors; and 25 55-gallon drums of debris. HELPER also holds a solid waste management
permit issued by the State of South Dakota Department of
Environment and Natural Resources ("DENR") under that State's
delegated authority pursuant to the Resource Conservation and
Recovery Act ("RCRA"). (Exs. 6, 9; Tr. 115-116).(1)
3. In order to obtain EPA approval to store PCBs, and its
State DENR permit, HELPER prepared a detailed Contingency-Spill
Prevention Control and Countermeasure Plan ("SPCC Plan"). The plan
was initially prepared in 1989 or 1990. It was revised several
times, including in February 1993. The February 1993 revision of
the SPCC Plan includes a material safety data sheet ("MSDS") for
PCBs, prepared by the chemical reference publisher, Genium
Publishing Company. The MSDS describes the chemical and physical
properties of PCBs. It also provides detailed information on the
proper procedures for storing and disposing of the material, and
for responding to spills, leaks, fires and other emergency releases
of PCBs. The MSDS also includes sections on the health hazards of
PCBs, and precautions for workers' protection from this substance.
The MSDS indicates that PCBs are considered a carcinogen by the
EPA. (Ex. 9, pp. O-P).
4. HELPER first sent copies of the SPCC to the DENR and the
Lake County Emergency Management Agency, at least by 1990. The
February 1993 revision that included the MSDS for PCBs was in the
hands of those agencies and the Madison Fire Department by February
1993. (Tr. 186-187, 194-195).
5. HELPER submitted a Tier II Emergency and Hazardous Chemical
Inventory form to the South Dakota SERC on October 20, 1994. The
form was signed by HELPER's environmental manager, Mike Yocum. The
inventory form listed PCBs as a hazardous chemical stored by
Respondent. The maximum daily amount listed was 100,000 pounds;
average daily amount 60,000 pounds; and maximum container capacity
125,000 pounds. The form also listed two other hazardous chemicals
present at the HELPER facility -- copper and 1,1,1,
trichloroethylene. The form also included a description and
diagrams of the PCB containers and storage area within the
facility. (Ex. 6).
6. The PCB-contaminated liquid in the transformers consists of
mineral oil dielectric fluid ("MODEF") also known as "mineral oil"
or "transformer oil," with a PCB content of from 50 to 499 ppm.
The maximum PCB concentration of 499 ppm, in terms of percentage,
is 0.05%, or five one-hundredths of one percent. The PCB
capacitors contain smaller amounts of highly concentrated PCB
liquids, up to 80% PCBs. An average capacitor weighs 75 pounds and
is comprised of from 5 to 10% of liquid. (Ex. 9, p G-9).
7. After receiving the used transformers, HELPER tests the
MODEF to ensure that the PCB content is between 50 and 499 ppm.
The PCB-contaminated liquids are then pumped into two 4000-gallon
tanks for storage, from where it is ultimately pumped into trucks
for disposal off-site. The MODEF is always in liquid form during
normal operations. The mineral oil containing PCBs at HELPER is
not present in the form of mist, or airborne droplets, although it
is possible that an oil mist could result from an accident, such as
the rupture of a hose under pressure. (Ex. 9; Tr. 251-254).
8. On October 15, 1992, at the time of an EPA inspection of
the facility HELPER had approximately 57,000 pounds of PCB-contaminated MODEF liquid in storage, approximately equal to its
maximum capacity of 8000 gallons. If those PCB-contaminated
liquids were at the maximum concentration of 499 ppm PCBs, the
amount of pure PCBs present would have been approximately 30
pounds. (Ex. 15). The remainder of the material was the
transformer oil, a type of mineral oil.
9. Mineral oils are distilled from naturally occurring crude
petroleum oils. The American Conference of Government and
Industrial Hygienists ("ACGIH") lists "Oil Mist, Mineral" as a
potentially hazardous substance used in the workplace, in its
publication of Threshold Limit Values ("TLVs"). That publication
assigns mineral oil mist a TLV of 5 milligrams per cubic meter of
air, expressed as a time-weighted average over an eight-hour work
day and a 40-hour work week. Mineral oil mists are generated in
certain industrial applications, such as metal working,
lubrication, textile machinery, rock drilling, printing inks,
rubber extenders, and pharmaceutical preparations. The TLV
represents an industrial hygiene guideline, establishing a
concentration to which nearly all workers may be repeatedly exposed
without adverse effect. (Exs. 3; 16, pp. iii, 1145; Tr. 236).
10. The HELPER facility was visited frequently by
representatives of the City of Madison Fire Department, the Lake
County Emergency Response Commission, and the South Dakota
Department of Environment and Natural Resources during the period
from 1988 to 1993. The Fire Department Chief, Dan Millard,
inspected the HELPER facility on April 29, 1993. Mr. Yocum,
HELPER's compliance manager, or Dan Pardy, its President, often
gave tours of the facility to these officials and to groups such as
the Madison Rotary Club. (Ex. 10; Tr. 123-127).
11. Dan Pardy, the President of HELPER, was initially a member
of the Lake County Emergency Management Agency, when it was first
established in 1985. In the years since, he has donated the
services and equipment of HELPER to the County Emergency Agency on
several occasions by helping in the clean up of small oil spills in
the Madison area. (Tr. 198-200).
Discussion
Count I of the Complaint charges that the Respondent did not
submit an MSDS for PCBs in a timely manner to the appropriate State
and local authorities, as required by EPCRA §311, 42 U.S.C. §11021,
and the regulations at 40 CFR Part 370. Count II alleges that
HELPER did not submit the hazardous chemical inventory form in a
timely manner to the same authorities, as required by EPCRA §312,
42 U.S.C. §11022.
HELPER argues that it is exempt from the requirements of both
statutes, since the hazardous chemicals present at its facility did
not meet the minimum threshold levels for reporting.
Alternatively, if it is not exempt, HELPER contends that it
substantially complied by fully informing the State DENR, Lake
County Emergency Management Agency, and City of Madison Fire
Department, of the presence of PCB-contaminated liquids at its
facility by submitting to those agencies copies of its SPCC which
included an MSDS for PCBs.
This decision finds that HELPER was exempt from these
reporting requirements because the quantity of hazardous chemicals
in its facility did not meet the minimum thresholds for reporting
or for being considered a hazardous chemical. Hence it is not
necessary to address in detail the issue of substantial compliance,
and both charges are dismissed.
On the date of the Region's inspection, October 15, 1992,
HELPER was storing near its permitted maximum amount of PCB-contaminated liquids -- approximately 8000 gallons or 57,000
pounds. It is not disputed that, if the PCBs in this liquid
mixture were at the maximum permitted level of 499 ppm, they would
weigh approximately 30 pounds. (Finding of Fact, or "FF," #8). It
is also not disputed that this maximum amount would comprise 0.05%
of the mixture. The remaining 99.95% of the mixture is mineral
oil. Under the EPCRA regulations for calculating the quantity of
hazardous chemical in a mixture, this amount of PCBs not only
doesn't meet the reporting threshold, but is not even sufficient to
be considered a hazardous chemical under the OSHA definition.
Facility owners or operators are required to submit an MSDS
and inventory form for hazardous chemicals present at the facility
at any one time in amounts equal to or greater than 10,000 pounds,
(or 500 pounds for extremely hazardous substances listed in 40 CFR
Part 355). 40 CFR §370.20(b)(1,2). A facility owner or operator
has the option of reporting on each component of the mixture that
is a hazardous chemical, pursuant to EPCRA §311(a)(3) and 40 CFR
§370.28. The calculation of the quantity, under §370.28(b)(1),
only requires reporting of chemicals that exceed 1% by weight of
the mixture, or 0.1% if carcinogenic. This provision tracks the
parallel OSHA regulation, at 29 CFR §1910.1200(d)(5)(ii), which
states as follows:
"If a mixture has not been tested as a whole to
determine whether the mixture is a health hazard, the
mixture shall be assumed to present the same health
hazards as do the components which comprise one percent
(by weight or volume) or greater of the mixture, except
that the mixture will be assumed to present a
carcinogenic hazard if it contains a component in
concentrations of 0.1 percent or greater which is
considered to be a carcinogen . . ."
Assuming that PCBs are carcinogenic, they still comprised less than
0.1% of the mixture in HELPER's stored transformers. They were
also far below the 10,000-pound EPCRA reporting threshold.(2) Thus,
the mixture as a whole would not be considered to present a
carcinogenic or health hazard unless the mineral oil is considered
a hazardous chemical.
Before addressing that question, it must be noted that the
Complaint specifically charged the Respondent only with not
reporting on PCBs in a timely manner. (Complaint, ¶¶6-8, 11-12).
The Complaint does not mention mineral oil, transformer oil, or any
other chemical besides PCBs. Under a narrow reading of the
charges, the inquiry could end here. However, the Region also
contends that the mixture as a whole should have been reported
because HELPER did not undertake a hazard determination for the
PCB-contaminated transformer liquids. Under this theory, HELPER
would have been required to report on the mixture as a whole, as a
PCB-contaminated mineral oil. HELPER did in fact submit an
inventory form in October 1994 that reported on the mixture as a
whole, as simply "PCBs."
The Region's argument would, in effect, hold Respondent
responsible for charges not made in the Complaint. For the time
period under consideration, 1992 and 1993, Respondent still had the
option to report on the components of its mixture, if they reached
the reportable thresholds. Under the mixture method, the
components in the PCB-contaminated MODEF do not meet the EPCRA
reporting threshold, and neither the components nor the mixture are
defined as hazardous under OSHA. Under the mixture and threshold
rules, the submittal of the 1994 inventory form was only an
optional, precautionary reporting. Regardless of how HELPER chose
to report in 1994, it was not required to submit an MSDS and
inventory form under EPCRA for the 1992-1993 period alleged in the
Complaint.
As an employer under the OSHA, HELPER was not required to
conduct its own hazard evaluation of its chemicals, but could rely
on information supplied by the chemical manufacturers, under 29 CFR
§1910.1200(d)(1). Although Mr. Yocum testified that he was unaware
of the requirement to conduct a discreet OSHA hazard determination,
HELPER did submit into evidence a representative MSDS for
transformer oil (Ex. 12). HELPER routinely included an MSDS for
PCBs in its SPCC, but not for the transformer oil. It is evident
that HELPER quite properly had sufficiently determined for all
practical purposes, although perhaps not formally, that the
transformer oil was not a hazardous chemical.
In any event, the Complaint did not charge HELPER with failing
to properly conduct a hazard determination under the OSHA. Rather,
the Complaint charged HELPER with not submitting an MSDS and
inventory form for PCBs or PCB-contaminated liquids as required by
EPCRA. The burden of proof was on the Region to show that
Respondent was required to report on its hazardous chemicals. The
Region failed to show that HELPER had reportable quantities of
hazardous chemicals on hand. Although it may have been desirable
for HELPER to make available an MSDS for mineral oil, as it did for
PCBs, as part of its SPCC plan, it was not required to do so by
EPCRA or OSHA. The evidence confirms the conclusion that
transformer oil, or mineral oil, is not a hazardous chemical, and
need not be reported in any quantity, or as part of a mixture.
The OSHA definition of hazardous chemicals, found in 29 CFR
§1910.1200(c), is incorporated by EPCRA §§311(e) and 312(c), as the
applicable definition for hazardous chemicals requiring the
submittal of an MSDS and inventory form. That regulation defines
hazardous chemical as "any chemical which is a physical hazard or
health hazard." Whether a chemical is a physical or health hazard
is determined by conducting a hazard determination under
§1900.1200(d). As discussed above, this can be done by relying on
information supplied by the chemical manufacturers, under
subsection (d)(1).
Pursuant to 29 CFR §1910.1200(d)(3), certain sources are
cited as authorities establishing that chemicals listed in them are
deemed hazardous. One of these is a publication by the American
Conference of Government and Industrial Hygienists ("ACGIH")
entitled Threshold Limit Values for Chemical Substances and Physical Agents in the Work
Environment ("TLV list"). This document is a comprehensive list of
hundreds of chemicals used in the workplace, with the ACGIH's
recommendations for safe levels of workers' exposure to these
substances. An excerpt of the TLV list that included the page for
"Oil Mist, Mineral" was received into evidence. (Ex. 3). The
relevant portion of the supporting Documentation for the oil mist
listing, and introductory material on the meaning and use of TLVs
was received as well. (Ex. 16).(3)
The Region argued that the ACGIH listing of a TLV for Oil
Mist, Mineral indicated that the transformer oil or mineral oil
stored by HELPER was itself a hazardous chemical subject to EPCRA
reporting under §§311 and 312. If this is so, HELPER would have
been required to report on it or the mixture as a whole. However,
a review of the TLV and the documentation reveals that the hazard
stems only from mineral oil in its airborne, or mist, form, as the
title of the listing indicates on its face. This corroborates the
testimony of Stephen Busch, P.E., Respondent's expert witness on
this issue, and statements on the transformer oil MSDS itself,
published by Texaco. (Ex. 12).
The ACGIH publication considers only mineral oil mist, not
liquids stored in tanks or containers. The TLV for mineral oil
mist is 5 milligrams per cubic meter of air, averaged over an 8-hour work day and 40-hour work week. (FF #9). The typical
applications cited by the ACGIH that generate oil mist include
metal working, textile machinery, drilling, and mist lubrication.
Electrical equipment is not mentioned. This standard has no
relation to the conditions of mineral oil storage at the HELPER
facility, where no mist is generated. (FF #7). At HELPER, the
mineral oil or transformer oil remains in liquid form in enclosed
tanks or containers at all times. Even in the unlikely event of an
accidental rupture, there would not be the type of continued
exposure contemplated by the ACGIH list of TLVs. The ACGIH's
listing thus indicates that mineral oil can be considered hazardous
only as a mist, not as an enclosed liquid.
The Region points out in its reply brief that HELPER was also
permitted to store PCB capacitors and other PCB-contaminated debris
and equipment. The Region has not, however, shown that Respondent
stored more than the threshold reporting amount of 10,000 pounds at
one time of such PCBs from all sources. Respondent is permitted to
store 3000 pounds of PCB-contaminated capacitors, plus 25 55-gallon
drums of debris. The capacitors could contain up to 10% by weight
of concentrated PCB-contaminated liquids, while the debris
typically contains little liquid. The capacitors are not opened,
but are stored in drums or on pallets. (Ex. 9, p. G-9). The PCBs
would still be far below the threshold reporting amount, and the
capacitors are probably exempt as "articles" under 29 CFR
§1910.1200(b)(1)(v). (See Ex. 2). In any event, the Complainant
focused only on the PCB-contaminated liquids from electrical
transformers and did not prove that the capacitors or other PCB
material met the reporting threshold.
In summary, the PCB-contaminated liquids stored by HELPER are
not defined as hazardous under EPCRA, which incorporates the OSHA
definition in 29 CFR §1910.1200(c). Since PCBs comprise less than
0.1% of the mixture and the remaining component, mineral oil, is
not a hazardous chemical, the mixture as a whole is not hazardous
under that definition. Other possible sources of PCBs stored by
HELPER, such as capacitors, were stored in amounts far below the
reporting threshold of 10,000 pounds. Hence, HELPER was not
required to submit an MSDS and inventory form for its PCB-contaminated liquids or other PCB materials in storage. Both
charges in the Complaint must therefore be dismissed.
- Subsidiary Issues
The Region was understandably misled to some degree by the
Respondent's filing of a Tier II inventory form in 1994 that
apparently reported on the PCB-contaminated liquids as a whole.
Since the amount exceeded 10,000 pounds, it appeared that
Respondent had failed to submit the form and/or the MSDS to the
three required State and local agencies in the prior years.
Respondent is not estopped, however, from now claiming it was
exempt, as the Region argues.
It does appear that Mr. Yocum, HELPER's compliance manager,
was not specifically aware of EPCRA reporting requirements, and
their possible relevance to his company, until a conversation with
Ralph Houck of EPA in July 1993. (Ex. 7). Only afterwards, when
HELPER answered the Complaint in this proceeding and analyzed the
PCB liquids present in its facility, did Mr. Yocum realize that its
chemicals did not meet the reporting threshold. Under the OSHA
definition, HELPER simply did not have reportable levels of hazard
chemicals on hand at any relevant time. The fact that HELPER may
have been ignorant of a law that did not apply to it, and then
attempted to comply although it was not required to, does not
change this reality.
This decision concludes that HELPER was not required to submit
an MSDS or inventory form under EPCRA §§311 and 312, since its
hazardous chemicals did not meet the reporting threshold.
Therefore, it is unnecessary to determine whether the Respondent
complied or substantially complied with these requirements anyway.
It will suffice to note that the record does not show definitively
exactly when the MSDS for PCBs was submitted to the State and local
authorities. (FF #4). Those authorities did, however, have copies
of HELPER's SPCC plan during the relevant period and were fully
aware of Respondent's storage of PCB-contaminated liquids. The
evidence shows Respondent submitted a Tier II inventory form to the
State DENR only in October 1994. These submittals of the MSDS and
inventory form are construed as optional and precautionary, in
light of the fact that HELPER was not required to file them under
EPCRA.
The Respondent also raised the defense of statute of
limitations in its pleadings and briefs. Again, it is not
necessary to address this issue in light of the decision that
Respondent was exempt from EPCRA reporting. Nevertheless, the
decision was based on the facts showing that HELPER did not have
threshold quantities of hazardous chemicals that required
reporting. If Respondent had been subject to reporting under EPCRA
§§311 and 312, any violation would have continued until at least
October 1992, the date alleged in the Complaint that Respondent had
a reportable amount of PCB-contaminated liquids present in its
facility.
Conclusion of Law
The Respondent, HELPER, did not have present in its facility
quantities of hazardous chemicals that met the threshold for
requiring submittal of an MSDS or inventory form pursuant to EPCRA
§§311 and 312, respectively.
Order
The charges alleged in the Complaint are dismissed.
Andrew S. Pearlstein
Administrative Law Judge
Dated: February 20, 1998
Washington, D.C.
1. Citations to the stenographic transcript ("Tr.") and exhibits ("Ex.")
are representative only, and not intended to be exhaustive.
2. Although PCBs are considered carcinogenic, they are not listed as an
extremely hazardous chemical in 40 CFR Part 355, which would subject them to a
500-pound reporting threshold or lower threshold planning quantity.
3. The documentation for the oil mist listing was the subject of official
notice by the Administrative Law Judge after the hearing, received over
Respondent's objection. The listing had been marked for identification
during the hearing as part of Exhibit 8, but inadvertently not received into
evidence.
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