Toxics Release Inventory Reporting Forms Modification Rule, 39931-39949 [05-13486]
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Federal Register / Vol. 70, No. 132 / Tuesday, July 12, 2005 / Rules and Regulations
2005. Filing a petition for
reconsideration by the Administrator of
this final rule does not affect the finality
of this rule for the purposes of judicial
review nor does it extend the time
within which a petition for judicial
review may be filed, and shall not
postpone the effectiveness of such rule
or action.
This action, approving the Virginia
section 111(d)/129 plan for small MWC
units, may not be challenged later in
proceedings to enforce its requirements.
(See section 307(b)(2).)
ENVIRONMENTAL PROTECTION
AGENCY
List of Subjects in 40 CFR Part 62
Environmental protection,
Administrative practice and procedure,
Air pollution control, Aluminum,
Fertilizers, Fluoride, Intergovernmental
relations, Paper and paper products
industry, Phosphate, Reporting and
recordkeeping requirements, Sulfur
oxides, Sulfur acid plants, Waste
treatment and disposal.
SUMMARY: To improve reporting
efficiency and effectiveness, reduce
burden, and promote data reliability and
consistency across Agency programs,
EPA is simplifying the Toxics Release
Inventory (TRI) reporting requirements.
TRI reporting is required by section 313
of the Emergency Planning and
Community Right-to-Know Act (EPCRA)
and section 6607 of the Pollution
Prevention Act (PPA). This rule
simplifies the TRI reporting
requirements by removing some data
elements from the Form R and Form A
Certification Statement (hereafter
referred to as Form A) that can be
obtained from other EPA information
collection databases, streamlining other
TRI data elements through range codes
and a reduced number of reporting
codes, and eliminating a few data
elements from the Form R. This rule
also makes two technical corrections to
the regulations to provide corrected
contact information and to remove an
outdated description of a pollution
prevention data element.
DATES: This rule is effective on
September 12, 2005. The first reports
with the revised reporting requirements
will be due on or before July 1, 2006, for
reporting year (i.e., calendar year) 2005.
ADDRESSES: EPA has established a
docket for this action under Docket ID
No. TRI–2004–0001. All documents in
the docket are listed in the EDOCKET
index at https://www.epa.gov/edocket.
Although listed in the index, some
information is not publicly available,
i.e., CBI or other information whose
disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available either electronically in
EDOCKET or in hard copy at the OEI
Docket, EPA/DC, EPA West, Room
B102, 1301 Constitution Ave., NW.,
Washington, DC. The Public Reading
Room is open from 8:30 a.m. to 4:30
p.m., Monday through Friday, excluding
legal holidays. The telephone number
Dated: June 29, 2005.
Donald S. Welsh,
Regional Administrator, Region III.
I
40 CFR part 62 is amended as follows:
PART 62—[AMENDED]
1. The authority citation for Part 62
continues to read as follows:
I
Authority: 42 U.S.C. 7401 et seq.
Subpart VV—Virginia
2. A new center heading, after
§ 62.11627, consisting of §§ 62.11635,
62.11636, and 62.11637 is added to read
as follows:
I
Emissions From Existing Small
Municipal Waste Combustor (MWC)
Units—Section 111(d)/129 Plan
§ 62.11635
Identification of plan.
Section 111(d)/129 plan for small
MWC units with capacities 35 to 250
tons per day, and the associated Virginia
Air Pollution Control Board Regulations
(Rule 4–46, and other supporting rules
identified in the plan), submitted to
EPA on September 2, 2003, including
supplemental information submitted on
August 11 and September 30, 2003;
April 6, 2004; and April 18, 2005.
§ 62.11636
Identification of sources.
The affected facility to which the plan
applies is each small MWC unit for
which construction commenced on or
before August 30, 1999.
§ 62.11637
Effective date.
The effective date of the plan for
small MWC units is September 12, 2005.
[FR Doc. 05–13700 Filed 7–11–05; 8:45 am]
BILLING CODE 6560–50–P
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40 CFR Part 372
[TRI–2004–0001; FRL–7532–6]
RIN 2025–AA15
Toxics Release Inventory Reporting
Forms Modification Rule
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
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39931
for the Public Reading Room is (202)
566–1744, and the telephone number for
the OEI Docket is (202) 566–1752.
FOR FURTHER INFORMATION CONTACT:
Shelley Fudge, Toxics Release Inventory
Program Division, Office of Information
Analysis and Access (2844T),
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460; telephone number: (202)
566–0674; fax number: (202) 566–0741;
e-mail address: fudge.shelley@epa.gov
for specific information on this
proposed rule. For more information on
EPCRA section 313, contact the TRI
Information Center, Toll free: (800) 424–
9346, TDD: (800) 553–7672, callers in
the DC area: (703) 412–9810.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does This Action Apply to Me?
This document applies to facilities
that submit annual reports under
section 313 of the Emergency Planning
and Community Right-to-Know Act
(EPCRA). It specifically applies to those
who submit the TRI Form R or Form A.
(See https://epa.gov/tri/report/
index.htm#forms for detailed
information about EPA’s TRI reporting
forms.) To determine whether your
facility is affected by this action, you
should carefully examine the
applicability criteria in part 372 subpart
B of Title 40 of the Code of Federal
Regulations. If you have questions
regarding the applicability of this action
to a particular entity, consult the person
listed in the preceding FOR FURTHER
INFORMATION CONTACT section.
This document is also relevant to
those who utilize EPA’s TRI
information, including State agencies,
local governments, communities,
environmental groups and other nongovernmental organizations, as well as
members of the general public.
II. What Is EPA’s Statutory Authority
for Taking These Actions?
This rule is being issued under
sections 313(g)(1) and 328 of EPCRA, 42
U.S.C. 11023(g)(1) and 11048; and
section 6607(b) of the Pollution
Prevention Act (PPA), 42 U.S.C. 13106.
In general, section 313 of EPCRA and
section 6607 of PPA require owners and
operators of facilities in specified SIC
codes that manufacture, process, or
otherwise use a listed toxic chemical in
amounts above specified threshold
levels to report certain facility-specific
information about such chemicals,
including the annual releases and other
waste management quantities. Section
313(g)(1) of EPCRA requires EPA to
publish a uniform toxic chemical
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release form for these reporting
purposes, and it also prescribes, in
general terms, the types of information
that must be submitted on the form. In
addition, Congress granted EPA broad
rulemaking authority to allow the
Agency to fully implement the statute.
EPCRA section 328 authorizes the
‘‘Administrator [to] prescribe such
regulations as may be necessary to carry
out this chapter.’’ 42 U.S.C. 11048.
III. What Is the Background and
Purpose of Today’s Actions?
A. What Are the Toxics Release
Inventory Reporting Requirements and
Who Do They Affect?
Pursuant to section 313(a) of the
Emergency Planning and Community
Right-to-Know Act (EPCRA), certain
facilities that manufacture, process, or
otherwise use specified toxic chemicals
in amounts above reporting threshold
levels must submit annually to EPA and
to designated State officials toxic
chemical release reporting forms
containing information specified by
EPA. 42 U.S.C. 11023(a). These reports
must be filed by July 1 of each year for
the previous calendar year. In addition,
pursuant to section 6607 of the
Pollution Prevention Act (PPA),
facilities reporting under section 313 of
EPCRA must also report pollution
prevention and waste management data,
including recycling information, for
such chemicals. 42 U.S.C. 13106. These
reports are compiled and stored in
EPA’s database known as the Toxics
Release Inventory (TRI).
The statute, along with regulations at
40 CFR part 372, subpart B, requires
facilities that meet all of the following
criteria to report:
• The facility has 10 or more full-time
employee equivalents (i.e., a total of
20,000 hours worked per year or greater;
see 40 CFR 372.3); and
• The facility is included in Standard
Industrial Classification (SIC) Codes 10
(except 1011, 1081, and 1094), 12
(except 1241), 20–39, 4911 (limited to
facilities that combust coal and/or oil
for the purpose of generating electricity
for distribution in commerce), 4931
(limited to facilities that combust coal
and/or oil for the purpose of generating
electricity for distribution in
commerce), 4939 (limited to facilities
that combust coal and/or oil for the
purpose of generating electricity for
distribution in commerce), 4953
(limited to facilities regulated under
Resource Conservation Recovery Act
(RCRA) Subtitle C, 42 U.S.C. 6921 et
seq.), 5169, 5171, and 7389 (limited to
facilities primarily engaged in solvents
recovery services on a contract or fee
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basis), or, under Executive Order 13148,
federal facilities regardless of their SIC
code; and
• The facility manufactures (defined
to include importing), processes, or
otherwise uses any EPCRA section 313
(TRI) chemical in quantities greater than
the established threshold for the specific
chemical in the course of a calendar
year.
Facilities that meet the criteria must
file a Form R report or in some cases,
may submit a Form A Certification
Statement for each listed toxic chemical
for which the criteria are met. As
specified in EPCRA section 313(a), the
report for any calendar year must be
submitted on or before July 1 of the
following year. For example, reporting
year 2003 data should have been
postmarked on or before July 1, 2004.
The list of toxic chemicals subject to
TRI can be found at 40 CFR 372.65. This
list is also published every year as Table
II in the current version of the Toxic
Chemical Release Inventory Reporting
Forms and Instructions. The current TRI
chemical list contains 582 individuallylisted chemicals and 30 chemical
categories.
B. Why Are We Modifying the Form A
Certification Statement and Form R?
EPA is modifying the TRI reporting
forms to improve efficiency and
effectiveness, reduce burden, and
promote data reliability and consistency
across Agency programs.
One of the purposes of today’s actions
is to reduce burden on facilities that
submit annual TRI reports without
compromising the data quality of toxic
chemical release and other waste
management information. ‘‘Burden’’ is
the total time, effort, or financial
resources expended by persons to
generate, maintain, retain, disclose, or
provide information to or for a federal
agency. 44 U.S.C. 3502(2). That includes
the time needed to review instructions;
develop, acquire, install, and utilize
technology and systems for the purposes
of collecting, validating, and verifying
information, processing and
maintaining information, and disclosing
and providing information; adjust the
existing ways to comply with any
previously applicable instructions and
requirements; train personnel to be able
to respond to a collection of
information; search data sources;
complete and review the collection of
information; and transmit or otherwise
disclose the information.
EPA has made considerable progress
in reducing burden associated with its
various information collections through
streamlining, consolidating and
harmonizing regulations, guidance and
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compliance assistance, and
implementing technology-based
processes (i.e., electronic reporting,
cross program data utilization, using
geospatial information to pre-populate
data fields). These measures have
reduced the time, cost, and complexity
of existing environmental reporting
requirements, while enhancing
reporting effectiveness and efficiency.
Today’s actions reduce the time, cost
and complexity of the reporting
requirements imposed on facilities.
While they are only expected to result
in a modest amount of cost and burden
savings, they also represent only the
first phase of a broader and more
substantive set of regulatory burden
reduction alternatives currently being
examined by EPA. That effort, described
in more detail below, is expected to
provide additional regulatory relief for
TRI reporters.
A second purpose of today’s rule is to
improve data reliability and consistency
across EPA programs. By replacing selfreported data from facilities with data
from EPA’s Facility Registry System on
items such as latitude and longitude and
facility ID numbers for other EPA
programs, EPA can better ensure that
this information is reported consistently
across programs and facilities. Further,
as locational information will have
method of collection, accuracy, and a
description of the location to which the
coordinates correspond (e.g., production
center, discharge point), data users will
be able to utilize information with
greater confidence. By streamlining
reporting requirements and improving
data reliability and consistency, this
rule will improve reporting efficiency
and effectiveness.
C. What Led to the Development of This
Rule?
Throughout the history of the TRI
program the Agency has implemented
measures to improve reporting
efficiency and effectiveness and reduce
the TRI reporting burden on the
regulated community. Through a range
of compliance assistance activities, such
as the Toxic Chemical Release Inventory
Reporting Forms & Instructions (which
is published and mailed every year),
industry training workshops, chemicalspecific and industry-specific guidance
documents, and the EPCRA Call Center
(a call hotline), the Agency has shown
a commitment to enhancing the quality
and consistency of reporting, and
assisting those facilities that must
comply with EPCRA section 313.
EPA has also done extensive work to
make reporting easier for the TRI
reporting community through the
development and use of technology,
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such as EPA’s Toxics Release
Inventory—Made Easy software,
otherwise known as ‘‘TRI–ME’’ (https://
www.epa.gov/tri/report/trime/). TRI–ME
is an interactive, user-friendly software
tool that guides facilities through the
TRI reporting process. By leading
prospective reporters through a series of
logically-ordered questions, TRI–ME
facilitates the analysis needed to
determine if a facility must complete a
Form R or A report for a particular
chemical. For those facilities required to
report, the software provides guidance
for each data element on Forms R and
A. TRI–ME has a one-stop guidance
feature, the TRI Assistance Library,
which allows keyword searches on the
statutes, regulations, and many EPCRA
section 313 guidance documents. TRI–
ME also offers a ‘‘load feature’’ that
enables the user to upload almost all of
the facility’s prior year data into the
current year’s report. Finally, TRI–ME
checks the data for common errors and
then prepares the forms to be sent
electronically over the Internet via
EPA’s Central Data Exchange (CDX).
TRI–ME generated reporting forms may
also be submitted offline via magnetic
media or on paper. In the spring of
2005, EPA distributed approximately
5,000 copies of TRI–ME in preparation
for the 2004 reporting year deadline of
July 1, 2005. Approximately 93% of the
roughly 98,000 Form Rs filed in 2004
were prepared using the TRI–ME
software.
In 1994, partially in response to
petitions received from the U.S. Small
Business Administration Office of
Advocacy and the American Feed
Industry Association, an EPA
rulemaking established the Form A
Certification Statement as an alternative
to Form R. This burden-reducing
measure was based on an alternate
threshold for quantities manufactured,
processed, or otherwise used by those
facilities with relatively low annual
reportable amounts of TRI chemicals.
For non-PBT chemicals, a facility may
use the Form A if the facility
manufactures, processes or otherwise
uses a TRI chemical below the alternate
threshold of one million pounds per
year and the facility has annual
reportable amounts of these toxic
chemicals not exceeding 500 pounds.
The annual reportable amount is the
total of the quantity released at the
facility, the quantity treated at the
facility, the quantity recovered at the
facility as a result of recycle operations,
the quantity combusted for the purpose
of energy recovery at the facility, and
the quantity transferred off-site for
recycling, energy recovery, treatment,
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and/or disposal. This combined total
corresponds to the quantity of the toxic
chemicals in production-related waste
(i.e., the sum of sections 8.1 through and
including section 8.7 on the Form R).
In an effort to further explore burden
reduction opportunities, EPA conducted
a TRI Stakeholder Dialogue between
November 2002 and February 2004. The
dialogue process focused on identifying
improvements to the TRI reporting
process and exploring a number of
burden reduction options associated
with TRI reporting. In total, EPA
received approximately 770 documents
as part of this stakeholder dialogue. Of
that, approximately 730 were public
comments and the remaining
documents were either duplicates or
correspondence transmitting public
comments to the online docket system.
The public comments expressed a range
of views, with some supporting burden
reduction and others opposing it. You
may view and obtain copies of all
documents submitted to EPA by
accessing TRI docket TRI–2003–0001
online at https://www.epa.gov/edocket or
by visiting the EPA docket reading room
in Washington, DC.
As a result of the Stakeholder
Dialogue, the Agency identified a
number of burden reducing options
which will continue to support existing
data uses and statutory and regulatory
obligations. These changes fall into two
broad categories: (1) Changes or
modifications to the reporting forms and
processes (including modifications to
the forms and improvements in the TRI–
ME software) which will streamline
reporting without significantly affecting
the information collected; and (2) what
the Agency believes are more
substantial changes that may affect
which facilities are required to report
and at what level of detail.
EPA decided to address the two
categories of changes through separate
rulemakings, one of which is today’s
action. This rule focuses on
streamlining reporting associated with
TRI’s Forms R and A. The changes
resulting from today’s action are the
elimination of some redundant or
seldom-used data elements from these
forms, and modification of other data
elements to reduce the time and costs
required to complete and submit annual
TRI reports. It also replaces some
elements with information from EPA’s
Facility Registry System in order to
improve data reliability and
consistency. EPA is confident these
changes will enhance the efficiency and
effectiveness of the TRI program by
reducing reporting requirements, while
continuing to provide communities and
other data users with the same, or
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higher quality, chemical release and
other waste management information.
The second rulemaking, to be
proposed later in 2005, will examine the
potential for more significant reporting
modifications with greater potential
impact on reducing reporting burden.
The options which may be considered
in that rulemaking include expanding
eligibility for Form A and introducing a
‘‘no significant change’’ option for
chemical reports that have not changed
significantly relative to a baseline
reporting year. Because of the greater
complexity and larger impacts
potentially associated with this latter
group of changes, additional analysis is
needed to more thoroughly characterize
its impact on TRI reporters and data
users.
IV. Summary of Today’s Final Rule
EPA is removing from the TRI Forms
R and A the latitude/longitude data
elements (section 4.6, Part I), the EPA
Identification Number(s) (RCRA ID No.)
(section 4.8, Part I), the Facility NPDES
Permit Number(s) (section 4.9, Part I),
and the Underground Injection Well
Code (UIC) ID Number(s) (section 4.10,
Part I). Instead of continuing to request
this information from the TRI reporter,
the Agency’s Facility Registry System
(FRS) will be used to populate the TRI
database with this information. This
information will continue to be made
readily available for all TRI reports and
applications such as the publicly
accessible TRI Explorer and all Form A
or R retrievals from Envirofacts at
https://www.epa.gov/enviro/
index_java.html. In other words, facility
identification and locational data will
still be made available for all reporters
and data users, but instead of requiring
facilities to supply their geographic
coordinates or provide certain EPA
program identification and permit
numbers, the Agency will extract this
data from information that is already
collected, stored and maintained in its
centrally managed database, the FRS.
Based on comments received and
information gathered since the proposed
rule, EPA is not removing from Form R
or modifying in any way, part II, section
5.3 column C as part of today’s rule.
Section 5.3 applies to discharges to
receiving streams and water bodies.
Column C requires facilities to indicate
the percentage of the total quantity of
the EPCRA section 313 chemicals
reported in column A (Total release)
that are discharged from stormwater.
As part of today’s action, the Agency
is, however, making modifications to
five data elements of part II, section 7
of the Form R. This rule simplifies
column B of section 7A—Waste
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Treatment Method(s) Sequence, by
replacing 64 codes used to describe the
various waste treatment methods
applied to EPCRA section 313 chemicals
treated on-site with a modified version
of the 18 hazardous waste treatment
codes (H040–H129), as they were
described in the proposed rule. These
18 codes are a modified version of the
codes used in EPA’s National Biennial
Resource Conservation Recovery Act
(RCRA) Hazardous Waste Report
(hereafter referred to as the RCRA
Biennial Report). (See PDF screen page
63 of the 2003 Hazardous Waste Report
Instructions and Forms (booklet) [EPA
Form 8700–13 A/B; 11/2000] available
at https://www.epa.gov/epaoswer/
hazwaste/data/br03/03report.pdf).
Based on comments submitted, several
modifications were made to the list of
H codes presented in the proposed rule.
For example, in the proposed rule EPA
inadvertently omitted treatment code
H083 (Air or steam stripping) from the
list of 18 hazardous waste treatment
codes. This was an oversight and EPA
has included this code in today’s rule.
Furthermore, ‘‘as the major component
of treatment’’ has been removed as a
qualifier from H082 (Adsorption as the
major component of treatment) and
H083 (Air or steam stripping as the
major component of treatment), ‘‘at
another site’’ has been removed as a
qualifier from H111 (Stabilization or
chemical fixation prior to disposal at
another site) and H112 (Macroencapsulation prior to disposal at
another site), and ‘‘only’’ has been
removed as a qualifier from H121
(Neutralization only).
In addition, based on comment
received on the proposed modification
to section 7A column B, EPA has
decided to retain the seven Air
Emissions Treatment codes currently
available for reporting in column B (see
page 55 of the 2004 TRI Reporting
Forms and Instructions (EPA 260–B–05–
001, January 2005) at https://epa.gov/tri/
report/index.htm#forms). Accordingly,
this rule finalizes the following list of
waste treatment codes for reporting in
part II, section 7A, column B of Form R:
A01 Flare
A02 Condenser
A03 Scrubber
A04 Absorber
A05 Electrostatic Precipitator
A06 Mechanical Separation
A07 Other Air Emission Treatment
H040 Incineration—thermal
destruction other than use as a fuel
H071 Chemical reduction with or
without precipitation
H073 Cyanide destruction with or
without precipitation
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H075 Chemical oxidation
H076 Wet air oxidation
H077 Other chemical precipitation
with or without pre-treatment
H081 Biological treatment with or
without precipitation
H082 Adsorption
H083 Air or steam stripping
H101 Sludge treatment and/or
dewatering
H103 Absorption
H111 Stabilization or chemical
fixation prior to disposal
H112 Macro-encapsulation prior to
disposal
H121 Neutralization
H122 Evaporation
H123 Settling or clarification
H124 Phase separation
H129 Other treatment
This rule eliminates section 7A,
column C—Range of Influent
Concentration from the Form R.
Today’s action allows facilities to
report their treatment efficiency as a
range instead of an exact percentage in
column D (Waste Treatment Efficiency
Estimate) of section 7A of Form R using
the following ranges:
E1 = greater than 99.9999%
E2 = greater than 99.99%, but less than
or equal to 99.9999%
E3 = greater than 99%, but less than or
equal to 99.99%
E4 = greater than 95%, but less than or
equal to 99%
E5 = greater than 50%, but less than or
equal to 95%
E6 = equal to or greater than 0% but less
than or equal to 50%
This set of ranges is different from the
set of ranges proposed. The ranges were
modified from the proposal to allow
data users to continue to distinguish the
performance of combustion devices in
excess of RCRA hazardous waste and
TSCA PCB incinerator standards. The
mid and lower range treatment
efficiencies were modified as well, in
response to comments to reduce the
number of categories in those ranges
and better reflect the distribution of
historical values.
This rule eliminates column E (Based
on Operating Data) of section 7A from
Form R.
This rule also removes the current
recycling codes for section 7C (On-Site
Recycling Processes) of the Form R and
replaces them with the following three
reclamation and recovery management
categories used in EPA’s RCRA Biennial
Report:
H10 Metal recovery (by retorting,
smelting, or chemical or physical
extraction)
H20 Solvent recovery (including
distillation, evaporation, fractionation
or extraction)
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H39 Other recovery or reclamation for
reuse (including acid regeneration or
other chemical reaction process)
See the PDF screen page 63 of the
2003 Hazardous Waste Report
Instructions and Forms (booklet) (EPA
Form 8700–13 A/B; 11/2000) available
at https://www.epa.gov/epaoswer/
hazwaste/data/br03/03report.pdf.
Readers will note that the actual code
numbers differ slightly from those in the
RCRA instructions in that the leading
‘‘0’’ (i.e., H020 ) has been removed from
each code name. This was done to avoid
the need to reprogram TRI–ME, thus
saving administrative costs. The Agency
does not believe this will cause any
confusion.
Today’s action also modifies section
8.11 of Form R by removing the
requirement to answer ‘‘yes’’ or ‘‘no’’ to
this optional section on additional
information on source reduction,
recycling, or pollution control activities.
Instead, an optional question will
replace the requirement to answer ‘‘yes’’
or ‘‘no’’ and an optional text box feature
will be added to EPA’s TRI–ME
reporting software to enable reporting
facilities to add a brief description of
their applicable source reduction,
recycling, and other pollution control
techniques and activities. Facilities will
still have the opportunity to submit
hard copies of any source reduction
information they may wish to submit.
Finally, through this rule EPA is
amending 40 CFR 372.85(a) to provide
a reference to the TRI Web site to obtain
the Form R instead of publishing in the
regulations an incorrect physical
address from which to request copies of
TRI forms. In addition, EPA will also
provide a phone number from which to
request TRI publications. EPA is also
deleting 40 CFR 372.85(b)(18), an
outdated pollution prevention data
element, which expired after the 1990
reporting year.
V. Summary of Public Comments and
EPA Responses
EPA received 31 distinctive
comments in response to this proposed
rule. While the majority of commenters
were supportive of today’s actions,
many commenters cautioned the
Agency to make sure that the changes
do not result in diminished data quality,
utility, or accessibility. Some
commenters urged the Agency to
consider data user needs and to balance
user needs with burden reduction. A
number of commenters also stated that
today’s actions will only provide
minimal burden relief, especially since
some of the changes are for information
that is collected by the facility one time
and used from year-to-year. Others
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expressed concerns about the initial
transaction costs that TRI reporters, as
well as the states, may incur to account
for these reporting changes and to
modify training materials and analysis
mechanisms already in place.
The TRI reporting form changes in
today’s rule support existing data uses
and fulfill statutory and regulatory
obligations. They are the first step in the
Agency’s larger effort to reduce
reporting burden for TRI reporters while
at the same time, these changes allow
the Agency to continue to provide
valuable information to the public
consistent with the goals and statutory
requirements of the TRI program. Some
of the changes being finalized today will
shift the burden to the Agency, and will
increase the quality of locational data
and EPA program identification
information (also referred to collectively
hereafter as facility identification
information). Other changes being
finalized today will reduce
computational burden, but maintain the
availability of information in a form
commensurate with its true underlying
precision. Accordingly, EPA does not
believe there will be a meaningful loss
of information for users.
While today’s changes provide only a
modest amount of burden relief, they
are important nonetheless, and based on
comments received, many TRI reporters
support this burden relief measure. EPA
is committed to all of its ongoing burden
reduction activities. As stated in the
proposed rule and above at Unit III.C.,
the Agency is pursuing a broader and
more substantive set of regulatory
burden reduction alternatives in a future
rulemaking.
EPA acknowledges that changes to the
TRI reporting forms could lead to some
initial transition costs for TRI reporting
facilities and other TRI stakeholders.
Balanced against this consideration, of
course, is the fact that these changes
will remove certain data elements from
the reporting forms and simplify others,
thereby making it easier for industry to
comply with the TRI reporting
requirements after the changes are
made. For example, whereas Form R
previously required reporters to
distinguish between three separate onsite wastewater treatment method codes
for cyanide oxidation, the changes
finalized today will allow reporters to
use one cyanide oxidation treatment
code. In addition, the initial burden
from adjusting to the form modifications
that the commenters predict will not
affect new reporters.
Further, EPA’s TRI–ME software can
be used by reporters to greatly ease
reporting burden. The software guides
reporters through a series of logically
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ordered questions that helps them
determine how to meet their regulatory
obligations, and provides various tools
for completing the reporting forms. The
changes finalized in today’s rule will be
incorporated into the TRI–ME software.
EPA does not require facilities or others
to develop additional data collection,
tracking or other databases or
documentation. Neither does the
Agency require any special training
materials or courses as a result of
today’s actions.
EPA does not believe that this rule
will impose significant burden on the
states. Most of the changes being
finalized are in the form of eliminating
data elements. The Agency will
continue to make all facility
identification data available through the
Facility Registry System (FRS).
Furthermore, the Agency will continue
to work with the states to improve
electronic information exchange
capability and the timeliness of such
exchanges.
EPA’s National Environmental
Information Exchange Network
(‘‘Exchange Network’’) provides state
partners the capability to access data
through a streamlined web services
process. As more states participate, they
will be provided with the ability to use
the Exchange Network’s built-in quality
checks, standard file formats, and a
common, user-friendly approach to
exchanging data. A majority of states
already take advantage of EPA’s
Exchange Network. In addition, we
expect numerous benefits to result from
the centralization of data in the
Agency’s FRS, which provides an
integrated, comprehensive source of
information about facilities subject to a
variety of environmental statutes and
regulations. As an essential part of
implementing this rule, EPA will
provide increased access to both the
FRS resources and the Agency’s
Integrated Error Correction Process
(IECP), so that states, facilities, and the
general public can more easily access
facility identification information and
report data errors when appropriate.
Finally, some commenters raised
issues about burden reduction (e.g., no
significant change certification criteria,
expanded eligibility for Form A) that
will be addressed in another rulemaking
(discussed above in Unit III.C.) to be
proposed later this year. Other
commenters raised issues unrelated to
this rulemaking (e.g., providing
additional context for the TRI data).
These comments are included in the
public docket for this rulemaking but
will not be addressed in this rule.
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A. Replacement of Certain Facility
Identification Data Reporting
Requirements (Sections 4.6 and 4.8
Through 4.10 of Forms R and A) With
Existing EPA Data From the EPA
Facility Data Registry
In the proposed rule, EPA requested
comment on removing reporting of
certain facility identification data
(latitude/longitude coordinates and
certain EPA program and permit
identification numbers) from the TRI
forms. Instead of collecting the data
annually from facilities, EPA would use
the centralized EPA database, known as
the Facility Registry System (FRS), to
populate the TRI database with this
information. Specifically, EPA proposed
populating the TRI database with
latitude and longitude information (also
referred to as locational data or
locational information) from the FRS.
Under this proposal, locational
information from FRS, including a
description of what the latitude and
longitude coordinates represent (e.g.,
center of production, pipe outfall, stack)
would be made readily available for all
TRI search applications, such as the
publicly accessible TRI Explorer and all
Form R and A retrievals from
Envirofacts. Similarly, as part of the
proposed rule, EPA requested comment
on automatically populating the TRI
database with EPA program and permit
identification numbers (except the TRI
facility identification number (TRIFID),
which facilities must continue to report
annually), from FRS as an alternative to
requesting the information from TRI
reporters. The program and permit
identification numbers that will be
populated from FRS include the
numbers assigned to facilities under the
Resource Conservation and Recovery
Act (RCRA), the permit identification
numbers under the National Pollutant
Discharge Elimination System (NPDES),
and the permit numbers issued by a
state to facilities with underground
injection control wells (UIC).
As discussed in the proposed rule, the
FRS is a centrally-managed database
developed by EPA’s Office of
Environmental Information (OEI). FRS
provides Internet access to a single
source of comprehensive information
about facilities that are subject to
environmental regulations and/or have
attributes that are of environmental
interest to EPA. The FRS database
currently contains over 1.5 million
unique facility records, and new
facilities are continuously being added
to the system, either through
information supplied by EPA programs
or through our state partners on the
Exchange Network. At this time, facility
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identification data are exchanged with
over three dozen states through the
Exchange Network. FRS also receives
correction and verification information
from the reporting community through
Web-based access, and through EPA
database systems, such as TRI,
maintained by over a dozen EPA
programs.
Eight commenters supported
removing the proposed facility
identification data from Forms R and A,
and instead, replacing these data
elements with data from the Agency’s
FRS so that TRI reporters would no
longer have to annually report these
data elements on their Form Rs or As.
Several commenters voiced support for
greater consistency between EPA’s
program databases, as well as increased
simplification and standardization of
the facility identification data that EPA
collects, stores and makes available to
the public. One commenter asserted that
this change would enhance TRI
reporting efficiency and improve data
quality, especially if existing databases
are utilized for populating Forms R and
A. Two commenters stated that these
changes would ease paperwork and
reporting burdens and lead to greater
consistency on data collection across
Agency programs. Several commenters
stated that the change would help
eliminate redundant data collection.
One commenter stated that the change
would promote wider use of the FRS.
Another commenter asserted that the
change should help avoid data entry
errors and promote consistent reporting
of facility locational data.
EPA agrees with the commenters that
the Agency’s databases should be
standardized and made consistent as
much as possible across various
programs. This regulatory change is part
of a larger Agency initiative to increase
the reliability and accuracy of the
Agency’s FRS database system.
Accordingly, EPA is finalizing its
proposal to use FRS to supply the data
for sections 4.6 and 4.8 through 4.10 of
Forms R and A.
Before finalizing this proposal,
however, EPA evaluated the concerns
expressed about ‘‘inherent flaws’’ in the
Agency’s FRS that compromise the
Agency’s efforts to consolidate
environmental data, minimize reporting
redundancies and create a single
identification system. Contrary to
statements in the proposed rule, one
commenter claimed that facility
identification records in FRS are not
accurate or authoritative. A commenter
asserted that this understanding is
supported by industry representatives
who must reconcile FRS data with
company records. A number of
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commenters emphasized that it was
imperative to enable the public to easily
retrieve all environmental information
about a specific facility.
Commenters did not provide data to
substantiate their claims of erroneous
information in FRS. Nevertheless, the
Agency examined FRS coverage of EPA
program identifiers in the context of
RCRA identification numbers (hereafter
referred to as RCRA IDs) to test the
commenters’ concern. The FRS database
contains all EPA program identification
numbers that are stored in EPA’s
national program system databases.
Regarding RCRA, FRS contains all the
RCRA IDs from the RCRAInfo database,
and is thus a definitive source for such
information. The Agency examined over
10,000 TRI forms with RCRA IDs from
the 2002 reporting year. A description of
this study is included below under Unit
V.A.2. of this preamble.
It is important to note here that the
FRS database covers all the TRI reports
for reporting year 2003 and has retained
all TRIFIDs (there are over 49,000 of
them) since the TRI program began in
the late 1980s. FRS also has the latitude
and longitude coordinates for all
historical TRIFIDs. The Burden
Reduction Rule will not impair the
public’s access to information about TRI
reporting facilities, including locational
data and EPA program identification
numbers. These data will continue to be
publicly available through various TRI
access tools. Only now they will be
supplied by the larger and more
authoritative data files in FRS. To the
extent that inconsistencies and errors
are identified in the future, the Agency’s
Integrated Error Correction Process
(IECP) will provide a convenient and
effective mechanism for bringing these
issues to the Agency’s attention for
resolution.
Two commenters asserted that
ideally, EPA should refrain from relying
on FRS to supply data to TRI until all
states are participating in the Exchange
Network and have the capability to
upload data into FRS. One commenter
stated that 14 states are still not active
in the Exchange Network. The
commenter asserted that data regarding
facilities in non-participating Exchange
Network states are not being scrutinized
by people most familiar with those
facilities. According to the commenter,
until all states are part of the network,
EPA lacks the ‘‘on-the-ground’’
intelligence needed to ensure that FRS
data is accurate or complete.
EPA agrees that ideally all the states
should be part of the existing Exchange
Network. However, we believe that the
commenter that urged EPA to wait to
implement this rule ‘‘until all states are
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participating in the FRS program’’ may
not have understood that FRS contains
data about regulated facilities’
identification information that has been
provided both by EPA’s many database
systems and by many state
environmental agencies. States do not
need to take any specific action to
access information data from FRS and
information is available in FRS for
facilities in states that aren’t yet a part
of the Exchange Network from various
EPA sources. Anyone, including state
agencies, can access data from FRS at
any time. While it is true that not all
states currently participate in the
Exchange Network, the vast majority of
states do participate, and EPA is
working closely with non-participating
states to help facilitate their full
participation in the near future.
Accordingly, EPA does not agree that
the rule should be delayed until all
states are participating in the Exchange
Network, nor does EPA agree that the
Agency lacks the ‘‘on-the-ground’’
intelligence needed to ensure that FRS
data are accurate or complete until such
time. The FRS is already functioning
and will be further enhanced as part of
the effort to implement this rule. EPA
will provide all states and other data
users the opportunity to correct
inaccurate TRI data. All states and
reporters will be able to correct
inaccurate information on locational
data and EPA program identification
numbers through the Agency’s
Integrated Error Correction Process
(IECP). As explained in the proposed
rule, another advantage of utilizing
information in the FRS is that one can
take advantage of EPA’s Public Internet
site to submit corrections to EPA’s data
on regulated facilities through one
central access point. The IECP unifies
the process by which EPA regulatory
programs manage error notifications to
the data in their systems. IECP is part of
an ongoing EPA effort to improve the
quality of EPA’s publicly available data.
Through the IECP, the public can
directly notify EPA of a data error
they’ve identified in EPA’s publicly
available data. They may notify EPA
through a variety of venues that include
the following: (1) Selecting the ‘‘Contact
Us’’ hotlink from the EPA Home Page
and accessing the link ‘‘report data
errors’’, (2) calling the IECP desk, (3)
sending a fax, or (4) e-mailing a detailed
description of the error.
Furthermore, the Agency will take
one additional step to ensure a smooth
transition to the use of FRS. For
reporting year 2004, the e-FDR is
expected to be publicly released in the
fall of 2005. At the time of the posting
of the individual TRI reporting form
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submissions (which will still contain
the collected facility identification data
elements), EPA will also post the facility
identification information stored in
FRS. This will enable interested parties
to directly observe the data and confirm
its accuracy. Lastly, the Agency will be
working closely with all states to ensure
a smooth transition to the utilization of
pre-existing facility identification data
in FRS.
One commenter recommended that
EPA delay implementing the use of FRS
to supply facility locational data and
EPA program identification numbers
until a pilot study is conducted to
ensure that these data are of equal or
higher quality in FRS than the data
which are contained in the TRI
database. In addition, according to the
commenter, problems arise when the
TRI dataset contains locational data for
facilities that FRS does not cover. While
having all states as part of the Exchange
Network may help address these
problems, the commenter asserted that
there are inherent limits to this kind of
after-the-fact reconciliation. The
commenter urged EPA to delay
implementation until the FRS dataset is
complete and the agency can ensure the
accuracy of the data.
While EPA does not agree that we
should delay using FRS to access TRI
facility identification information until
a pilot study can be undertaken, a
separate assessment was conducted of
locational information in FRS versus
that contained in the TRI database. The
locational information in the two
systems was compared on the basis of
performance against two criteria: A
quality screening approach and
conformance to the Agency’s data
standards for locational information.
Absent very detailed site information,
it is difficult to design a locational
screening test. What the Agency did was
to compare the locational data stored in
FRS versus such data in the TRI
database on a county basis (i.e., what
percentage of reported locational data
were within the boundaries of the
counties where the facilities’ street
addresses were located). While it is
possible for a street address to vary
appreciably from the location of the
facility’s center of production, the
Agency believes this test provides a first
approximation of relative performance.
We found that 98% of all FRS locational
data as opposed to 97% of all TRI
locational data met this criterion.
Therefore, on the basis of this broad
measure, the two systems had
comparable information.
For the second test, the Agency
looked at how the data conformed with
the Agency’s data standards for
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locational information (i.e., a
description of the method of data
collection and what is measured, as well
as probable accuracy). Fully 89% of all
TRI facility locational data for reporting
year 2003 would have been able to meet
the Agency’s data standard
requirements if FRS had been used to
derive TRI locational data. Currently,
none of the TRI locational data can meet
the Agency’s data standards for
locational information, which require
metadata for the method, accuracy and
description of what the latitude and
longitude coordinates represent.
Over the coming months, the Agency
is implementing a program to ensure
that virtually all TRI facilities will have
locational information that meet the
Agency’s data standard requirements.
An implementation plan describing this
program has been included in the
docket that accompanies this rule.
Furthermore, through the IECP, EPA
provides the opportunity to correct
inaccurate data maintained for use by
TRI data users.
1. Removal of Latitude/Longitude
Reporting Requirement (Section 4.6 of
Forms R and A). Three commenters
recommended that reporters be
provided the opportunity to review and
correct the latitude/longitude data
stored in EPA’s FRS before removing
section 4.6 from the reporting forms and
replacing it with locational data from
FRS. One of the commenters also
recommended that EPA keep FRS
locational data updated in a timely
manner.
While EPA does not agree with the
commenters’ suggestion on waiting for
facilities to review their locational data
before removing part I section 4.6 from
the TRI reporting forms, EPA
wholeheartedly agrees with the
commenters that TRI reporters should
be allowed to review and correct their
latitude/longitude data in FRS. We are
taking a number of steps to provide this
opportunity. Specifically, in the fall of
2005, at the time of the electronic
facility data release (eFDR), we will be
providing the relevant FRS locational
information along with the responses
provided by the facility for the 2004
reporting year. This will enable all
interested parties, including data
reporters and users to compare the
information contained in the most
recent TRI submission with the
corresponding information for that
facility in FRS.
Any interested party will have the
opportunity to raise concerns with TRIreported latitude/longitude values or the
new values to be derived from FRS.
These concerns may be submitted to the
Agency through the IECP (discussed
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39937
above). The Agency plans to improve
access to the IECP to make it very easy
for TRI reporters or data users to review
and notify the Agency of inaccurate
locational values.
One commenter cautioned EPA that
the definition of ‘‘facility’’ under EPCRA
is not necessarily the same as the
definition of ‘‘facility’’ under other
statutes, and that this could affect the
use of FRS data. The commenter
asserted that under EPCRA two sites
that are adjacent and/or contiguous and
that are owned by the same entity are
considered to be one facility (even if
separated by a public road). However,
according to the commenter, under
RCRA the sites would be considered
two facilities. As such, there may be
instances where the data from each
source is different for the same
‘‘facility.’’
Variation in facility definitions as one
crosses EPA program boundaries is one
of the major challenges the Agency faces
in its efforts to develop a central facility
registry. However, it is a challenge
which already faces some users of TRI
information. For example, users of
information for RCRA assessments are
already faced with the challenge to
create a map between multiple RCRA
facilities and a single TRI facility, when
the facility definitions are not
consistent. Likewise, there may be cases
where the TRI-reported RCRA IDs do
not constitute the totality of RCRA IDs
associated with a given TRIFID due to
a limited number of spaces on the TRI
form. Presently, crosswalk checks are
completed manually.
The conversion to the use of FRS for
facility identification information
should actually strengthen the mapping
across programs with different facility
definitions. To understand why this is
so, one needs to understand the
meaning of a facility in FRS. In FRS,
each entity with a discrete street address
is an independent facility. Where
individual programs will disagree is in
the case of more complex facilities
where ownership or programmatic
considerations have led to the clustering
of multiple FRS ‘‘facilities’’ into a single
entity for the purposes of a program
(e.g., TRI).
A key step in the transition to the use
of FRS supplied locational data will be
the creation of a program map. This map
will use the 2004 TRI responses to
assign a TRI facility identification
number (TRIFID) to each relevant FRS
facility. Where multiple FRS facilities
have the same TRIFID, all will be
assigned the same TRIFID. This map
will ensure that the locational
information for the TRI facility contains
not only all relevant locational
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information, but also all relevant EPA
program identification numbers.
Furthermore, the locational information
retrieved will be superior to current TRI
information because it will have
metadata describing how the
information was derived, its collection
method, its probable accuracy, and a
geographic description (i.e., whether it
is based on the center of the production
facility, a pipe outfall, stack, etc). This
change will provide a much more
comprehensive look at all of the
locational information for TRI facilities.
Furthermore, the enhanced access to the
IECP for data suppliers and users should
result in a steady improvement in
facility mapping and locational
information.
One commenter was troubled about
how long it would take to populate FRS
with TRI data and complete data quality
checks. The commenter urged EPA to
ensure that no lapses occur in the
availability of locational data as a result
of this process.
EPA will ensure that there is no lapse
in making locational data available for
TRI data users. Locational data from TRI
and other programs is already stored in
FRS and the Agency will provide a
seamless transition from collecting
locational data directly from TRI
reporters to pulling existing locational
data out of FRS and providing it along
with other facility identification
information to TRI data users starting
with the public data release for
reporting year 2005 information, which
must be submitted by July 1, 2006.
Several commenters expressed
concern that EPA’s FRS database does
not often have previously stored
locational data for first-time TRI
reporters. The commenter asserted that
this data gap problem could also be
exacerbated by the fact that not every
state is participating in EPA’s Exchange
Network. The commenter recommended
that EPA modify the rule to require
reporting of locational data by first time
reporters. Another commenter stated
that data gaps in the FRS database could
be best addressed by requiring new
reporting entities to include additional
information on facility identification
data the first time they are required to
complete Form R or A.
EPA acknowledges that there are a
relatively small number of new facilities
that submit TRI Form R or A reports
each year for which the Agency does not
already have locational data stored in
FRS. The Agency disagrees, however,
that new reporters should be required to
submit locational data. EPA plans to use
street address matching in combination
with its siting tool to populate FRS with
locational data for those cases in which
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FRS has no previous locational data for
new reporters. As discussed above,
reporters, as well as the states and the
general public will be provided the
opportunity to submit a request for
correcting inaccurate facility locational
data by using the Agency’s IECP.
Two commenters opposed the use of
address matching for deriving TRI
facility latitude/longitude data. One
commenter stated that the two most
apparent problems with this method
are: (1) If the facility is in a rural or
unpopulated area, offshore, etc., then
the software may be unable to match the
address to a location; and (2) the
facility’s mailing address may not be the
location where the toxic chemical
releases occur. For example, if a facility
picks up mail at a headquarters building
that manages several facilities, this
would create a different latitude/
longitude than where its stacks are
located.
The second commenter claimed that
as much as 70% of the locational data
derived from various EPA databases and
stored in FRS may be based on address
matching. The commenter maintained
that some of the locational data in FRS
may be based on wastewater outfall
locations that can be long distances
from the facilities. Reliance on FRS data
collected from these other databases,
according to the commenter, would
introduce significant error into the use
of the information.
The Agency disagrees with these
commenters. Dealing with the second
comment first, FRS does not use mailing
addresses for locational referencing of
facilities. Rather, the actual street
address of the facility is used. EPA
believes that street address matching,
used in combination with our facility
siting tool (i.e., a geospacial application
that uses aerial imagery to determine
latitude and longitude coordinates) in
rural areas, can provide credible
locational coordinates for all TRI
facilities. EPA plans to use this method
for new reporters and for other cases in
which no credible locational data is
available in FRS. The Agency believes
that this method provides a better
source of data than locational data for
which there is no metadata (i.e., no
explanation as to how the information
was derived or its accuracy), which
occurs with the current locational data
reported to the TRI program.
Furthermore, because the Agency plans
to include all locational information in
the next e-FDR, anyone interested in a
particular facility will be able to easily
raise concerns through the IECP with
the data chosen to represent the location
of the facility.
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As to the concern with the quality of
FRS, FRS has been operational since
2000 and continues to improve data
quality. Many EPA programs utilize FRS
and the existing IECP process is in place
to facilitate receipt of suggested
corrections to locational information.
Despite these facts, only a very small
percentage of IECP requests have
involved locational updates. Further, for
smaller facilities, especially those most
likely to rely on street addresses, we
believe an address is a reliable indicator
of location.
Further, FRS will provide a complete
picture of all locational information
available on a facility. Because FRS
provides metadata for the method,
accuracy, and description of its
locational data, it will be possible to
know exactly the nature of the point
being measured. The data user of such
information will know whether they are
using a point based on an outfall, a
stack, or the center of the production.
To the extent that a preferred location
reported out of FRS is incongruent with
the intended use of the TRI information,
the data user may simply use another
locational value for their purposes. This
is a significant improvement on the
current TRI locational values of
unknown accuracy and relevance.
One commenter recommended that
instead of removing section 4.6 from the
TRI reporting forms, facilities should
instead certify that the latitude and
longitude data reported to TRI is
obtained either from EPA’s Facility
Siting Tool or from a Global Positioning
System (GPS) device. According to the
commenter, this would ensure that
facilities provide more accurate
information.
The Agency does not agree with the
commenters that there is an issue with
the accuracy of locational information
in FRS. Furthermore, we do not agree
that increasing reporting burden on TRI
reporters to provide locational data that
is already available in FRS is an
appropriate response. Transitioning to
FRS use for locational information will
allow users to not only have the most
current locational information, but a
clear indication of the method of
collection, description of what is
measured, and probable accuracy. They
will know the reference point of the
facility (e.g., the street address, a stack,
or some permitted portion of the
facility) for which locational
information is provided. Finally, use of
FRS will improve the overall quality of
TRI facility locational information. FRS
will be continuously gathering the best
locational information based on
metadata for the method, accuracy and
description of what the latitude and
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longitude coordinates represent—
including GPS-based data—as opposed
to relying only on TRI-reported values
of unknown precision. Furthermore, as
stated in response to several previous
questions, the IECP will provide yet
another means for continually
improving facility identification
information.
2. Removal of Reporting Requirements
for EPA Permit and Program
Identification Numbers (Sections 4.8,
4.9 and 4.10 of Forms R and A). Three
commenters emphasized the importance
of EPA facility identification numbers to
TRI data users, including various EPA
program offices and the general public.
One commenter cited, as an example,
the use of Resource Conservation and
Recovery Act (RCRA) identification
numbers to calculate ‘‘double counting’’
of TRI chemical disposal transfers sent
to TRI facilities that report the same
chemicals again. The commenter stated
that RCRA Identification numbers
(RCRA IDs) allow transfers of chemicals
(marked with RCRA IDs in section 6 of
Form R) to be matched up with
receiving TRI facilities (marked with
RCRA IDs in section 4.8). The
commenter also cited a 1998 report by
a public interest organization to
demonstrate the usefulness of collecting
EPA program identification numbers in
TRI. The report used the Underground
Injection Control identification numbers
to help analyze the completeness and
accuracy of underground injection well
data in EPA databases. According to the
commenter, these examples are just a
small sample of the many uses for this
data. The commenter recommended that
EPA conduct a small study to
demonstrate that FRS data is of equal or
higher quality to TRI’s program
identification data before removing
these data elements from the TRI
reporting forms.
EPA agrees with the commenters that
the EPA program identification numbers
in sections 4.8 through 4.10 of the TRI
reporting forms are important and are
used extensively by various EPA offices,
the states, and the general public. This
information will not be lost. Program
identification numbers previously
reported through TRI are already stored
in the TRI database known as the Toxics
Release Inventory System (TRIS) and
will be available to data users through
access tools offered by the Agency.
Nevertheless, in consideration of
commenters’ concerns, EPA conducted
a study of RCRA IDs and concluded that
FRS provided higher data quality than
TRI reporting. In particular, the Agency
examined over 10,000 TRI forms with
RCRA IDs from the 2002 Reporting Year.
These facilities were selected because
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they were used by the Office of Solid
Waste in its annual evaluation of waste
minimization progress for
approximately thirty chemicals related
to a Federal Government Performance
and Result Act (GPRA) goal. In its
evaluation, the Office of Solid Waste
uses the RCRA IDs in conjunction with
Form R sections 5 and 6 data to estimate
the quantities of priority chemicals that
may be contained in hazardous versus
non-hazardous wastes. This activity is
analogous to those of interest to the
commenters.
Approximately 800 RCRA IDs were
found in the TRI database that did not
match RCRA IDs in the RCRAInfo
database. Almost half of these RCRA IDs
contained obvious transcription errors
(i.e., ‘‘o’’ substituted for ‘‘zero’’, etc). It
is not clear to what extent the remainder
represent more subtle transcription
errors or other factors, although it is
important to note that the Office of
Solid Waste maintains an active data
stewardship program. On the other
hand, it is also important to note that
the TRI Reporting Form has only two
spaces for the listing of RCRA IDs.
Because of differences in facility
definitions, it is quite reasonable to
assume that a current TRI facility could
be associated with more than two RCRA
IDs. Given these factors, and the fact
that FRS contains RCRA IDs assigned by
EPA’s RCRA program, there can be little
doubt that FRS is a more definitive
source of information on RCRA IDs, and
that cross program coverage will be
improved by conversion to the use of
FRS.
We believe that the few cases in
which there may be information gaps
can be addressed by improving
communication between EPA’s Office of
Environmental Information, which
operates both the TRI and FRS
programs, and the other Agency offices
responsible for the program
identification data at issue. The one
possible exception to this statement
relates to IDs for underground injection
sites reported under the UIC program.
Presently, UIC IDs are not collected on
the Federal level except as a part of TRI.
States maintain these records.
Unfortunately, because of form
limitations, TRI reporters have not
necessarily provided a full listing of UIC
permitted wells. EPA’s Office of
Information Collection is working with
the Office of Ground Water and
Drinking Water, however, to gather UIC
information from individual states to
include in FRS. It is anticipated that
states will begin to provide this more
complete information in 2006, in
advance of the first data release to be
affected by this rule.
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One commenter expressed concern
about a time lag in the availability of
EPA program identification data if EPA
removes the program identification
numbers from the TRI reporting forms.
The commenter cited the importance of
this data to a variety of community
groups across the country and urged
EPA to quickly address this potential
problem so the public would not
experience a lag in its use of TRI
Explorer.
As discussed above, the FRS already
stores EPA program identification data.
EPA will ensure that there is no lag in
the availability of such data in TRI
Explorer or Envirofacts, the two EPA
data applications that TRI data users
rely upon to access TRI-related data. By
the time that the 2006 TRI Public Data
Release (PDR) is published, all
applicable FRS data will have been
copied into the TRI database for
publication.
One commenter asserted that the EPA
program identification numbers on the
TRI reporting forms are used by state
environmental agencies as a cross
reference for other program
applications. According to the
commenter, at least one state uses the
data as a link to hazardous waste
generator reporting, in addition to its
use as a key identifier for TRI facilities.
The commenter expressed concern that
the proposed rule did not address how
states would receive these data elements
if they are not supplied with the Form
R. The commenter contended that many
states have developed their own data
systems to manage the TRI reports filed
with the state and they regard TRI
reporting as a joint EPA-State
partnership since facilities are required
to file their forms at both the Federal
and State levels. The commenter
expressed concern that the data
elements states need to manage their
TRI data will be lost if this change is
finalized.
EPA is committed to ensuring that
states and TRI data users have accurate
program identification numbers
associated with TRIFIDs. To ensure that
these data are available to states in a
timely fashion after the TRI report is
filed with EPA’s Reporting Center, the
Agency will use the Exchange Network
to share data with states using the web
services available through the Central
Data Exchange (CDX). For states that
may not yet be web-enabled, EPA will
make available other electronic means
to retrieve program identification
numbers for the TRIFIDs of interest.
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B. Reporting Requirement for
Determining the Percentage of the Total
Quantity of Toxic Chemicals
Contributed by Stormwater (Part II,
Section 5.3 Column C)
In the proposed rule, EPA asked for
comment on removing part II, section
5.3 column C from Form R. This data
element applies to discharges to
receiving streams and water bodies.
Column C requires facilities to indicate
the percentage of the total quantity of
the EPCRA section 313 chemicals
reported in column A (Total release to
that water body) that are discharged due
to stormwater. Column C was the only
part of section 5.3 affected by this
proposal. Changes to the rest of part II,
section 5.3 were not included in this
proposal.
A number of commenters supported
the removal of column C, claiming that
this data element is difficult to
accurately estimate. Others in favor of
removing column C from Form R
asserted that there does not appear to be
any significant use of this data element
by the public or other TRI stakeholders.
Three commenters, however, opposed
removing section 5.3, column C. One
commenter noted that this data element
is important to understanding periodic
spikes in overall water releases that may
be caused by stormwater run-off.
According to this commenter, directing
data users to the NPDES system to
obtain this information is not an
adequate option because integrating
data across EPA’s databases is not an
easy task. Further, the commenter
asserted that phosphate mining stacks
may be an example of a sector that is not
part of the NPDES system but reports
significant quantities of toxic chemicals
contributed by stormwater. The
commenter requested EPA to examine
whether there are other sectors for
which the public cannot get the same
data from NPDES before eliminating this
data element.
Another commenter stated that it is
not uncommon for the overall water
releases reported in TRI to rise or fall
because of a few facilities with large
releases associated with stormwater.
The commenter contended that
stormwater runoff often dominates such
large releases, and the inclusion of this
data element allows users to better
understand what drives year-to-year
variations in water release data, and to
detect whether increases were due to
production changes or rainfall.
According to the commenter, if column
C were to be removed TRI data users
would have to cobble together
information about the percentage of
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stormwater contribution from various
EPA database sources.
Yet another commenter stated that
these particular percentages have been
useful to the public when making yearto-year comparisons of discharges to
water. According to this commenter,
these numbers can vary wildly from
year-to-year, and having information
about the percentage attributed to
stormwater runoff, versus the amount
that could be attributed to a discharge
of toxic chemicals, is critical
information for the public. The
commenter asserted that this proposed
change represents a significant loss of
data.
Based on the public comments
received and additional information that
has recently come to light from EPA’s
Office of Water, the Agency now better
understands how this data element is
used by EPA program offices, states,
communities, researchers and other TRI
data users. The Agency has thus
decided not to remove column C of
section 5.3 from Form R. While EPA
acknowledges that it may be difficult for
some facilities to estimate the
percentage of the total quantity of toxic
chemicals contributed by stormwater,
EPA believes that this data element
provides important information that
helps researchers, communities and
other TRI data users make year-to-year
comparisons of discharges of toxic
chemicals to water that is unavailable
elsewhere. One example of how these
data are used comes from the Division
of Engineering and Analysis in EPA’s
Office of Water, which uses this data
element in its pollution control
activities and the Agency’s biennial
report to Congress under section 304 B
of the Clean Water Act.
As to the availability of this
information from other sources, the
commenters were again divided. There
clearly are areas of non-coverage by
other databases and, at a minimum, it
would be difficult to pull the
information together in one place to
inform the public and other data users.
Furthermore, even if the information
could be pulled together in one place,
there inevitably would be difficulties
introduced by trying to harmonize TRI
and NPDES release totals between two
databases that may have differences in
assumptions or measurement
approaches. We believe the continued
collection of this data element best
fulfills the EPCRA reporting goals of the
program and therefore, EPA will not be
finalizing the proposal to eliminate
column C of section 5.3, part II of the
Form R.
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C. Modifications to the Reporting
Requirement for On-Site Waste
Treatment Methods and Efficiency and
On-Site Recycling (Part II, Section 7A
and Section 7C)
As explained in the proposed rule,
section 313(g)(1)(C)(iii) of EPCRA states
that facilities must report ‘‘for each
wastestream, the waste treatment or
disposal methods employed, and an
estimate of the treatment efficiency
typically achieved.’’ 42 U.S.C.
11023(g)(1)(C)(iii). Data elements
collecting waste treatment information
and related details, such as whether the
efficiency estimate was based on
operating data, were implemented
through a 1988 rule. 53 FR 4516–18
(Feb. 16, 1988). For recycling activities,
section 6607(b)(2) of the PPA states
facilities must report ‘‘the amount of the
chemical * * * which is recycled * * *
and the process of recycling used.’’ 42
U.S.C. 13106(b)(2). Facilities fulfill
these obligations, in part, by reporting
qualitative information regarding their
on-site waste treatment and recycling of
EPCRA section 313 chemicals in part II,
section 7 of the Form R.
In the proposed rule EPA asked for
comment on the following
modifications to part II, section 7 of the
Form R:
(1) Simplifying column B of section
7A (Waste Treatment Method(s)
Sequence) by replacing 64 codes used to
describe the various waste treatment
methods with a modified version of the
18 hazardous waste treatment codes
currently used in EPA’s RCRA Biennial
Report;
(2) Eliminating column C of section
7A (Range of Influent Concentration);
(3) Simplifying column D of section
7A (Waste Treatment Efficiency
Estimate) by replacing the requirement
to submit an exact percentage with a
range code;
(4) Eliminating column E of section
7A (Based on Operating Data); and
(5) Simplifying section 7C (On-Site
Recycling Processes) by replacing 16
codes used to report particular recycling
methods with 3 reclamation and
recovery codes used in EPA’s RCRA
Biennial Report.
EPA received comment on each of
these five proposed modifications. A
summary of these comments and
responses to them are addressed in turn
in the following sections.
1. Part II, Section 7A—On-Site Waste
Treatment Methods and Efficiency
(Column B—Waste Treatment
Methods(s) Sequence). EPA received a
number of comments in response to the
proposal to simplify column B of
section 7A—Waste Treatment Method(s)
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Sequence, by replacing the 64 codes (see
page 55 of the 2004 Toxic Chemical
Release Inventory Reporting Forms and
Instructions (EPA 260–B–05–001,
January 2005) at https://epa.gov/tri/
report/index.htm#forms) used to
describe the various waste treatment
methods applied to EPCRA section 313
chemicals treated on-site with a
modified version of the 18 hazardous
waste treatment codes (H040-H129)
currently used in EPA’s National
Biennial RCRA Hazardous Waste
Report, also known as the RCRA
Biennial Report. (See page 63 of the
2003 Hazardous Waste Report
Instructions and Forms (booklet) [EPA
Form 8700–13 A/B; 11/2000] available
at https://www.epa.gov/epaoswer/
hazwaste/data/br03/03report.pdf).
A majority of the commenters
supported reducing the number of onsite waste treatment codes, claiming that
this change will reduce burden for TRI
reporters. Further, by making the
reporting codes consistent with the
RCRA Biennial Report, TRI reporting
will be made easier for those facilities
familiar with RCRA.
EPA agrees with the commenters that
reducing the number of on-site waste
treatment codes and making them more
consistent with the reporting codes used
in EPA’s RCRA Biennial Report will
result in less reporting burden for TRI
reporters. The vast majority of
comments submitted about this section
of the proposal confirmed EPA’s belief
that facilities recognize and appreciate
EPA’s efforts to provide more
consistency between its various
reporting requirements and program
activities. The comments also confirmed
our belief that there would be no
significant loss of data quality if the
codes were consolidated.
One commenter supported the
proposed change but cautioned that it
would actually increase the burden of
TRI reporting since not all facilities file
RCRA Biennial Reports, and these
facilities may be unfamiliar with the
RCRA codes. The commenter expressed
concern about those reporters who
would have to familiarize themselves
with the new codes and revise their TRI
analysis accordingly. This commenter
was also concerned that reporters that
fill out both TRI annual and RCRA
biennial reporting forms would still
have an initial period where TRI
analysis mechanisms already in place
would have to be adjusted.
EPA appreciates the commenter’s
concern regarding those reporters
unfamiliar with the reporting codes in
the RCRA Biennial Report. EPA
believes, however, that in the vast
majority of cases, facilities will be
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familiar with these codes. As explained
in the proposed rule, eighty percent of
TRI reporters report a RCRA
identification number on Form R, part I,
section 4.8. The majority of facilities
with an assigned RCRA identification
number also file a RCRA Biennial
Report. While there may be an initial
period of adjustment, EPA believes that
the long-term burden reduction benefits
greatly surpass any short-term
drawbacks. To facilitate a smooth
transition, EPA will include additional
information in the annual TRI reporting
forms and instructions manual. The
instructions will define each of the new
codes, explain the few minor differences
that exist between the new TRI codes
and the RCRA Biennial Report codes,
and describe the relationship between
the old treatment codes and the new
ones.
Some commenters opposed the
proposal to replace the 64 waste
treatment codes with the 18 codes used
in the RCRA Biennial Report. One
commenter recommended that EPA not
use the RCRA H treatment codes and
instead, use a shorter, more concise list
of codes.
EPA disagrees with the commenter
that a shorter list of codes should be
used for section 7A column B instead of
the RCRA H treatment codes. We
believe that since the majority of TRI
reporters also report their hazardous
waste treatment methods in EPA’s
RCRA biennial reporting process, a
consistent use of reporting codes will
result in more reduced reporting burden
than shortening the current TRI list of
codes. During the development of the
proposed rule, the Agency considered
reducing the number of RCRA H
treatment codes for Form R, but we
decided that a slightly modified version
of all 18 different RCRA H treatment
codes is needed to adequately capture
the various types of hazardous waste
treatment methods used by facilities.
Another commenter expressed
opposition to reducing the number of
treatment codes, emphasizing the desire
for accurate reporting rather than
‘‘simplified’’ reporting. A second
commenter stated general opposition to
this proposed change contending that
such a change would represent a loss of
data.
EPA disagrees with these
commenters. No specific information or
compelling examples were provided by
commenters regarding potential data
loss if the treatment codes in section 7A
column B were reduced and made
consistent with the hazardous waste
treatment codes used in the Agency’s
RCRA Biennial Report. Rather, EPA
believes that this change will improve
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39941
data quality because it will prevent
reporters from over-specifying their
treatment trains. Consequently, EPA
will replace the 64 waste treatment
codes with a modified version of the 18
hazardous waste H treatment codes used
in the RCRA Biennial Report (plus
seven air emission treatment codes as
discussed in the following paragraphs)
for use in section 7A, column B of Form
R.
Some commenters who were
generally supportive of the proposal to
use the RCRA treatment codes, raised
specific concerns. For example, ten
commenters expressed concerns
regarding the removal of air emissions
treatment codes in the proposed
consolidated treatment codes for section
7A, column B. Several of these
commenters recommended that the
Agency retain the seven air emissions
treatment codes (A01 to A07) currently
used for reporting in Section 7A,
column B. Many commenters stressed
their concern about the lack of codes to
cover the treatment of gas streams,
which one commenter asserted was the
primary means by which utilities reduce
their toxic chemical releases, and the
primary waste treatment method used at
electric power plants. Another
commenter stated that since the on-site
treatment of acid aerosols are among the
most voluminous gas streams reported
in Section 8.6, it was especially
important to make air emissions codes
in section 7A column B available to
accurately capture this type of
treatment. Without specific air emission
codes, they maintained that facilities
would have to use the code for ‘‘other
treatment’’ (H129) and this code would
not provide any useful information to
TRI data users.
EPA agrees with the commenters that
it is important to adequately describe
the treatment methods used for air
emissions and gas streams. Based on the
comments submitted, the Agency better
understands and appreciates the
necessity to include air emissions codes
in section 7A column B of Form R.
While EPA proposed the complete
consolidation of the treatment codes in
section 7A column B to make them
consistent with the hazardous waste
codes used in the RCRA Biennial
Report, we inadvertently overlooked the
fact that the RCRA codes don’t cover air
emissions very well. EPA agrees with
the commenters that a substantial
amount of valuable data would be lost
if the seven existing codes for air
emissions were to be removed.
Consequently, this final rule retains the
seven existing air emissions codes used
in section 7A column B.
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Several commenters questioned why
EPA omitted one of the RCRA H
treatment codes, H083, from the list of
18 hazardous waste treatment codes
proposed for use in section 7A column
B. Several of these commenters
requested that EPA clarify whether this
was an intentional omission.
EPA inadvertently omitted treatment
code H083 from the list of 18 hazardous
waste treatment method codes that were
proposed to replace the existing 64
treatment codes in section 7A, column
B of Form R. EPA recognizes the need
to include treatment code H083 to
capture air or steam stripping treatment
and has included this code in the final
rule.
One commenter questioned how the
phrase used in a parenthetical in the
proposed treatment code H083 ‘‘(as the
major component of treatment),’’ would
apply in sequential on-site treatment
methods where the approach is simply
one step in a multi-step process. The
commenter noted that the same
parenthetical phrase might be applied to
proposed treatment code H082 as well
if EPA used that code in the final rule.
This commenter contended that since
several of the other treatment codes
proposed for use in section 7A column
B did not include the parenthetical
phrases used in the RCRA Biennial
Report, ‘‘(as the major component of
treatment),’’ should be omitted from
codes H082 and H083 as well.
EPA appreciates receiving the
comment requesting clarification on the
use of the parenthetical phrase ‘‘as the
major component of treatment’’ at the
end of the treatment codes H083 and
H082. EPA agrees that the use of this
parenthetical may cause confusion
regarding sequential on-site treatment
methods where the approach is simply
one step in a multi-step process.
Consequently, EPA has removed the
parenthetical ‘‘as the major component
of treatment’’ from H083 (Air or steam
stripping) and H082 (Adsorption).
A commenter requested that EPA
clarify the use of the RCRA hazardous
waste treatment codes H111
(stabilization or chemical fixation prior
to disposal at another site) and H112
(macro-encapsulation prior to disposal
at another site) in section 7A column B.
The commenter noted that the use of the
phrase ‘‘at another site’’ would pose a
problem for TRI reporting facilities with
on-site landfills, as well as for facilities
that use stabilization for the final
treatment of their wastes. The
commenter recommended that the
phrase, ‘‘at another site’’ be removed
from the treatment code description in
the final rule.
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EPA agrees with the commenter and
is removing the phrase, ‘‘at another site’’
from the description for treatment codes
H111 (Stabilization or chemical fixation
prior to disposal) and H112 (Macroencapsulation prior to disposal). We
agree that the use of the phrase ‘‘at
another site’’ would unnecessarily
restrict the use of these codes to waste
intended to go off-site, and believe that
the removal of this phrase will avoid
confusing reporters who otherwise can
use these codes to describe their on-site
treatment methods.
Four commenters requested
clarification of proposed treatment code
H121—Neutralization only. They
pointed out that the word ‘‘only’’ would
eliminate the use of this code by
facilities that use neutralization as one
of several steps in a sequence of waste
treatment methods, rather than as the
single method of treatment. One
commenter contended that such a
restriction would force facilities that use
it as one of several waste treatment
method steps, to use treatment code
H129—Other treatment. Two
commenters requested that EPA
consider removing the word ‘‘only’’
from the treatment code description for
H121. Another commenter suggested
that the word ‘‘only’’ is relevant to
reporting under the RCRA Biennial
Report and does not serve the purposes
of TRI reporting.
EPA agrees with the commenters
regarding the use of the word ‘‘only’’ in
the description of proposed treatment
code H121. We acknowledge that the
word could restrict the use of that code
unnecessarily and force facilities that
use neutralization as one of several
steps in a sequence of waste treatment
methods to instead use treatment code
H129—Other treatment. EPA believes
that more useful information can be
derived from the proper use of treatment
code H121 than H129 by facilities that
use neutralization as either their only
treatment method or as one of several
steps in their waste treatment process.
The Agency has thus removed the word,
‘‘only’’ from the H121 treatment code
description to be used in section 7A
column B.
In accordance with all of the above,
this rule finalizes the following list of
waste treatment codes for reporting in
part II, section 7A, column B of Form R:
A01 Flare
A02 Condenser
A03 Scrubber
A04 Absorber
A05 Electrostatic Precipitator
A06 Mechanical Separation
A07 Other Air Emission Treatment
H040 Incineration—thermal
destruction other than use as a fuel
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H071 Chemical reduction with or
without precipitation
H073 Cyanide destruction with or
without precipitation
H075 Chemical oxidation
H076 Wet air oxidation
H077 Other chemical precipitation
with or without pre-treatment
H081 Biological treatment with or
without precipitation
H082 Adsorption
H083 Air or steam stripping
H101 Sludge treatment and/or
dewatering
H103 Absorption
H111 Stabilization or chemical
fixation prior to disposal
H112 Macro-encapsulation prior to
disposal
H121 Neutralization
H122 Evaporation
H123 Settling or clarification
H124 Phase separation
H129 Other treatment
2. Part II, Section 7A—On-Site Waste
Treatment Methods and Efficiency
(Column C—Range of Influent
Concentration). As discussed in the
proposal to eliminate section 7A,
column C—Range of Influent
Concentration, EPA explained that
column C was implemented in the 1988
rule in which EPA initially published
the Form R. 53 FR 4518. During the
development of the 1988 rule, EPA
believed that concentration information
would assist users in determining
whether effective treatment methods
may be available for wastes containing
different amounts of a given chemical
because the effectiveness of most
treatment methods is concentrationdependent. See Proposed Rule, 52 FR
21152, 21163 (June 4, 1987). Further, an
indication of influent concentration
would aid in the evaluation of treatment
methods across industries and therefore
put the data into better perspective. 53
FR 4518. As expressed in the proposal,
contrary to the intended uses of this
information, EPA has not identified a
specific Agency use for the information
in section 7A, column C and does not
believe that this information is widely
used by states or the public.
To date, completion of column C
requires facilities to enter a numerical
code, from the following list, indicating
the concentration range of the EPCRA
section 313 chemical as it enters the
treatment step:
1 = Greater than 10,000 parts per
million (1%)
2 = 100 parts per million (0.01%) to
10,000 parts per million (1%)
3 = 1 part per million (0.0001%) to 100
parts per million (0.01%)
4 = 1 part per billion to 1 part per
million
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5 = Less than 1 part per billion
In the proposed rule, EPA also asked
for comment on whether as an
alternative reporting under section 7A,
column C should be optional, with
facilities having a choice as to whether
to report the influent concentration
range of the EPCRA section 313
chemical.
Sixteen commenters expressed
support for removing the range of
influent concentration data element
under section 7A column C. One
commenter asserted that this change
would provide the most significant
amount of burden reduction of all the
changes proposed in this rule. Several
commenters stated that calculating these
concentrations for each EPCRA section
313 chemical (or chemical category) in
each waste stream is very time
consuming and often requires numerous
assumptions. One commenter asserted
that facilities have spent upwards of 40
hours or more to report on this data
element, reflecting the significant
burden associated with this
requirement.
Commenters also contended that the
resulting data are of little value to the
general public. One commenter stated
that since certain facilities, like power
plants, do not normally sample the
concentrations of various process
streams before treatment occurs, the
reported values in column C are
estimates that have little value to the
general public. Commenters claimed
that the removal of the range of influent
concentration would not result in a
significant loss to the TRI community.
In response to this proposed removal of
column C of section 7A, one commenter
stated that data users can determine
from the remaining information in
section 7A that a facility has a given
chemical in its influent and that it is
treating that chemical with a specific
treatment method to a specific
percentage range of efficiency.
Commenters maintained that removing
this data element would not impact the
usefulness of the waste treatment
efficiency estimate in Column D.
Further, several commenters
expressed support for entirely removing
the data element rather than providing
an option to report this data element.
They contended that allowing for such
an option would create confusion
among reporters and inconsistencies in
the TRI database. One commenter added
that it is unlikely that facilities would
provide data should the requirement to
report data in Column C be made
optional.
EPA agrees with the commenters that
removing the data element for range of
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influent concentration under section 7A
column C would reduce a significant
amount of burden for TRI reporters. We
acknowledge that a large number of
facilities do not collect monitoring data
and instead, provide estimates for this
data element on influent concentration.
The Agency also appreciates the
information provided by commenters
regarding whether this data element
should be made optional. We agree with
the commenters that such an option
could create confusion among reporters,
and due to the inconsistent amount of
data that would be reported, we believe
that it would provide information of
very limited value to the public.
In the proposal, EPA stated its belief
that this information is not widely used
by states and the public as was
anticipated when this data element was
first included on Form R. EPA did not
receive any comments that opposed the
removal of this data element, nor any
comments that provided information on
the extent of its use or why the data
element was important to retain.
Therefore, EPA believes that its original
1988 assumptions that this information
would be valuable to the public have
not been substantiated and has decided
to finalize the elimination of this data
element.
3. Part II, Section 7A—On-Site Waste
Treatment Methods and Efficiency
(Column D—Waste Treatment Efficiency
Estimate). As discussed in the proposal,
the waste treatment efficiency
(expressed as a percentage) reported in
section 7A column D represents the
percentage of the TRI chemical
destroyed or removed (based on amount
or mass). Under EPCRA section
313(g)(1)(C)(iii), facilities are required to
submit an estimate of the treatment
efficiency typically achieved by the
waste treatment or disposal methods
employed for each waste stream. To
date, facilities are required to enter an
exact percentage in this column of the
form. In the proposed rule EPA asked
for comment on allowing facilities to
report their treatment efficiency as a
range instead of an exact percentage.
The Agency proposed using the
following ranges in column D:
E1 = greater than 99.9%
E2 = greater than 95% to 99.9%
E3 = greater than 90% to 95%
E4 = greater than 75% to 90%
E5 = greater than 30% to 75%
E6 = 0% to 30%
This proposed set of ranges was
developed by analyzing a subset of the
treatment efficiencies reported in
reporting year 2002. Most of the
efficiencies were between 90% and
100%. The proposed range codes reflect
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39943
this reporting trend by grouping three of
the codes between 90% and 100% and
having the other three codes represent
larger ranges between 0% and 90%.
Commenters expressed general
support for allowing TRI reporters to
use range codes instead of a specific
percentage number in section 7A
column D. Several commenters claimed
that a single value estimate suggests far
greater certainty about removal
efficiencies than exists in the real world
and that it is difficult to estimate a
precise percentage for the treatment
efficiency of the method used by a
facility. Another commenter stated that
since electric utility power plants
operate in a variety of different ways
over the course of a year and because
fossil fuels are heterogeneous, a single
treatment efficiency value is nothing
more than a long-term average value.
One commenter contended that the use
of ranges is a more reasonable approach,
and covers any variance in the treatment
efficiencies. The commenter added that
the use of ranges would avoid the
appearance of a precise estimate when
the estimate was actually based on
professional judgment.
EPA agrees with the commenters that
allowing ranges to be reported in section
7A column D provides a more realistic
estimate of on-site waste treatment
efficiency. We believe that the use of
ranges will provide burden relief to
facilities that currently find it difficult
to estimate an exact percentage due to
the reasons pointed out by commenters
regarding facility operations. We do not
believe that this change will result in a
loss of data since the data element will
still consist of an estimate of the
treatment efficiency typically achieved
by the waste treatment or disposal
methods employed for each waste
stream. We believe it will instead more
accurately reflect the treatment
efficiency variations that occur over the
course of a facility’s yearly operation.
One commenter asserted that the use
of range codes for treatment efficiencies
would not be a labor saver since its
emissions-estimating-software already
calculates the overall treatment
efficiencies. A second commenter stated
that in order to report within one of the
ranges proposed by EPA, a facility must
still undergo the analysis required to
obtain an exact percentage. The
commenter noted that this is
particularly true in the higher ranges,
where most reported efficiencies fall.
The commenter concluded that burden
reduction would not result from this
change.
EPA disagrees with these commenters
that little, if any, burden would be
eliminated as a result of this change.
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The majority of commenters supported
this change, asserting that it is difficult
to derive an exact treatment efficiency
percentage estimate for this data
element. Even for facilities with access
to sophisticated emissions-estimating
software that allows faster calculations
of emissions estimates, such software
does not necessarily capture the
uncertainty in the estimate, and even
those facilities may realize a reduction
in burden through the use of ranges.
One commenter asserted that the
proposed change in section 7A column
D could create problems with reporting
in other sections of Form R. As an
example, this commenter referred to
problems with the use of ranges in
sections 5 and 6 of Form R. According
to the commenter, when the ranges in
those sections are compared against the
values reported in section 8 of Form R,
the values do not balance (e.g., often the
use of range codes will result in a
‘‘NOTE’’ error on the Facility Data
Profile, because the software evidently
uses the midpoint of the range).
EPA disagrees with this comment.
EPA does not believe that the use of
range codes in section 7A column D will
affect reporting in other sections of the
form, such as sections 5, 6 or 8.
However, EPA will review the TRI–ME
and data quality software to ensure that
this change does not create errors in
data processing.
Two commenters opposed the change
to range codes in section 7A column D
due to general concerns about the use of
range codes. One of these commenters
stated that the use of range codes in
section 7A column D would represent a
loss of data. The commenter said that
range codes would also limit
information without reducing the
amount of time and resources a facility
would need to estimate its efficiency.
The second commenter stated that range
codes set a bad precedent and this
commenter had difficulty understanding
how range codes would reduce burden
since facilities would still need to
calculate the general efficiency
percentage in order to determine the
appropriate range.
EPA disagrees with these
commenters. Range reporting is already
used in a variety of Form R data
elements and we do not believe that
applying range code reporting to this
data element will set any kind of
precedent that would degrade the
quality of TRI data. As many
commenters noted, the data reported in
section 7A column D are generally
based upon an estimate, rather than
specific monitoring data. We believe
that the use of range codes in this data
element will more accurately reflect an
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estimated value without sacrificing data
quality.
Two commenters who supported the
proposed change expressed concern
about the limited number of ranges
provided in the high-end of the
proposed ranges. They prefer that EPA
either allow TRI reporters, particularly
incinerators, to report a specific on-site
waste treatment efficiency percentage
estimate, or that EPA provide additional
efficiency percentage range categories at
the upper end of the range scale. These
commenters claimed that this was
necessary to prevent un-permitted
incinerators that do not meet RCRAmandated treatment efficiencies for
some chemical wastes, to report in the
highest performing efficiency range.
According to these commenters, the
absence of these additional upper-end
range categories would result in
accurate but misleading information
that would be contrary to the goals of
Community Right-to-Know and arguably
the Data Quality Act. The commenters
asserted that the absence of these
additional upper-end ranges would
contradict the Agency’s attempt to meet
the Pollution Prevention Act’s goal of
allowing the public to understand the
ultimate destruction of toxic chemicals.
Both commenters recommended that if
upper ranges are used instead of
allowing reporters to use specific
percentages, the ranges should be
changed to the following: greater than
99.9% to 99.99%, greater than 99.99%
to 99.9999%, and greater than
99.9999%.
EPA appreciates receiving specific
recommendations and agrees with the
commenters that some adjustments
should be made to the proposed upper
ranges of treatment efficiency estimates
for use in section 7A column D. We
have used similar, although not exactly
the same treatment efficiency ranges as
those proposed by the commenters. The
upper-level ranges that EPA used in the
final rule include the following: Greater
than 99% to 99.99%, greater than
99.99% to 99.9999%, and greater than
99.9999%. These ranges were selected
in order to ensure an equal distribution
of the range categories, and to allow
data users to continue to distinguish the
performance of combustion devices in
excess of RCRA hazardous waste and
TSCA PCB incinerator standards. EPA
believes that these revised range
categories will provide a means for
those TRI reporters who are achieving a
high degree of treatment efficiency to
communicate that desirable outcome to
the public. EPA does not believe that
this level of specificity will diminish
the burden saving associated with the
use of ranges because facilities in the
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high-efficiency ranges will have readilyavailable knowledge about the
efficiency of their processes since those
high efficiencies are required by other
programs’ regulatory standards. EPA is
not going to allow TRI reporters,
however, to report a specific percentage
amount in section 7A column D since it
could result in two sets of confusing
data that would be impossible to
combine for any meaningful assessment.
Four commenters supported the
proposed change but recommended
reducing the total number of ranges
used in section 7A column D. These
commenters favored reducing the
number of ranges in the mid-range.
Three of the commenters proposed
combining proposed ranges E2 (greater
than 95% to 99.9%) and E3 (greater than
90% to 95%), so that there would be
one category that covers greater than
90% to 99.9%. One commenter
recommended changing the proposed
ranges to 0 to 50%, greater than 50% to
90%, greater than 90% to 99%, and
greater than 99%.
In response to the comments on
modifying the ranges, in this rule EPA
has reduced the number of reporting
ranges for the lower and mid-ranges
from four categories to two categories
(greater than 0% to 50% and greater
than 50% to 95%). However, the
Agency cannot agree to consolidate the
upper range codes. If, as the
commenters suggested, the Agency
consolidated greater than 90% to 99.9%
into one range, over half of all
respondents would be in that category.
By dividing the ranges into greater than
0% to 50%, greater than 50% to 95%,
and greater than 95% to 99%, the new
categories will represent 18%, 20% and
29%, respectively of all responses. EPA
believes these ranges provide a balance
that is adequate for realizing burden
reduction, while simultaneously
distinguishing major differences in
treatment performance.
Based on all of the above, EPA is
finalizing the following ranges for use in
part II, section 7A, column D:
E1 = greater than 99.9999%
E2 = greater than 99.99% but less than
or equal to 99.9999%
E3 = greater than 99% but less than or
equal to 99.99%
E4 = greater than 95% but less than or
equal to 99%
E5 = greater than 50% but less than or
equal to 95%
E6 = equal to or greater than 0% but less
than or equal to 50%
4. Part II, Section 7A—On-Site Waste
Treatment Methods and Efficiency
(Column E—Based on Operating Data).
As discussed in the proposed rule,
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column E of section 7A requires
facilities to indicate ‘‘Yes’’ or ‘‘No’’ as to
whether the waste treatment efficiency
reported in section 7A, column D is
based on actual operating data such as
the case where a facility monitors the
influent and effluent wastes from this
treatment step. When this data element
was first implemented, EPA believed
that this information would be valuable
to users because it would indicate the
relative quality and reliability of the
efficiency estimate figure (see 52 FR
21152, 21163). EPA explained in the
proposed rule that it is unaware of any
significant use of this data. EPA thus
proposed eliminating column E of
section 7A of Form R.
Several commenters supported the
removal of section 7A, column E. Two
commenters stated that if the proposed
changes to section 7A, columns C
(Range of influent concentration) and D
(Waste treatment efficiency estimate)
were finalized, then the data in column
E would not provide meaningful data to
the public. Another commenter asserted
that most of their treatment efficiencies
are based on company-derived
estimated efficiencies rather than on
monitoring data.
EPA agrees with the commenters that
section 7A, column E would not provide
meaningful information to the public
without specific percentage estimates in
section 7A, column D. Since the
proposed modification of column D to
range codes is being finalized through
this rule for the reasons discussed
above, and because EPA did not receive
any comments on the usefulness of
column E data, EPA has finalized the
elimination of column E.
5. Part II, Section 7C—On-Site
Recycling Processes. As discussed in the
proposed rule, facilities that conduct
on-site recycling currently use sixteen
codes (see page 58 of the 2004 TRI
Reporting Forms and Instructions (EPA
260–B–05–001, January 2005) at https://
epa.gov/tri/report/index.htm#forms) to
report the particular recycling method(s)
applied to each EPCRA section 313
chemical being recycled on-site. For
each Form R filed, facilities may report
up to ten ‘‘R’’ (On-site recycling) codes,
as appropriate.
EPA proposed eliminating these
sixteen recycling codes and replacing
them with the following three
reclamation and recovery management
codes used in EPA’s RCRA Biennial
Report:
H010 Metal recovery (by retorting,
smelting, or chemical or physical
extraction)
H020 Solvent recovery (including
distillation, evaporation, fractionation
or extraction)
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H039 Other recovery or reclamation
for reuse (including acid regeneration
or other chemical reaction process)
For further information about the
RCRA reclamation and recovery
management codes, see EPA’s RCRA
Biennial Report, which can be found at:
https://www.epa.gov/epaoswer/
hazwaste/data/br03/03report.pdf. See
the PDF screen page 63 of the 80 page
report.
Fourteen commenters supported
reducing the number of on-site recycling
codes for use in section 7C. Several
commenters stated that such a change
would promote consistency between the
RCRA hazardous waste and TRI
reporting programs. One commenter
stated that this change would reduce
unnecessary complexity. Several
commenters expressed support for the
change because they felt that the three
proposed codes adequately cover the
range of recycling activities that might
be undertaken at a facility. In addition,
the vast majority of commenters
contended that the change would not
compromise the utility of TRI program
data.
EPA appreciates receiving comments
that confirmed the Agency’s belief that
the use of fewer codes will simplify
reporting in section 7C of Form R.
Further, by making the TRI reporting
process more consistent with the RCRA
biennial reporting process we will
facilitate even greater use of data in both
the TRI and RCRA programs. Based on
these comments, EPA has finalized this
proposed change. However, in order to
avoid software reprogramming costs, the
Agency has decided to maintain a three
digit numerical code for this data
element, and thus, will not use the first
zero in each of the three RCRA
reclamation and recovery management
codes. Otherwise, the codes will
conform with the reclamation and
recovery management codes in the
RCRA Biennial Report. The codes to be
used in part II, section 7C of Form R
will thus be as follows:
H10 Metal recovery (by retorting,
smelting, or chemical or physical
extraction)
H20 Solvent recovery (including
distillation, evaporation, fractionation
or extraction)
H39 Other recovery or reclamation for
reuse (including acid regeneration or
other chemical reaction process)
D. Removal of Reporting Data Field for
Optional Submission of Additional
Information (Part II, Section 8.11).
As discussed in the proposal, section
6607(d) of the Pollution Prevention Act
(PPA) requires that reporters be
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39945
provided the opportunity to include
‘‘additional information regarding
source reduction, recycling, and other
pollution control techniques’’ with their
reporting form. 42 U.S.C. 13106(d). At
the present time, EPA requires each
facility to answer a ‘‘yes/no’’ question to
indicate whether the facility has
included such information. Facilities
with such information then attach a
physical copy describing their activity.
Because such information is long and in
varied forms, it has not been coded into
the TRI database. This lack of coding
creates a large potential burden for users
of information seeking to identify
innovative programs or processes.
Accordingly, EPA proposed minor
changes to this data element to improve
public access to such information.
As explained in the proposal, an
optional text box feature would be
added to EPA’s TRI–ME reporting
software to enable reporting facilities to
submit a brief description of their
applicable source reduction, recycling,
and other pollution control techniques
and activities. In addition, reporters
would be provided with instructions in
EPA’s ‘‘Toxic Chemical Release
Inventory Reporting Forms’’ on how to
denote on their Form R submission that
they are providing a brief summary and/
or more detailed information on one of
these activities. Form R would be
modified to include a checkbox
allowing facilities that provide
additional information to check ‘‘yes’’ if
they use the text box feature or send
EPA additional information in
hardcopy. Facilities that do not wish to
provide additional information would
no longer need to check ‘‘no’’ in section
8.11.
With this revision, EPA would make
this additional information available on
the Agency’s public access Web site for
the first time, through one of EPA’s
system applications, such as
Envirofacts. This change would provide
TRI data users with improved access to
the additional information that facilities
submit about their source reduction,
recycling, and other pollution control
techniques.
Several commenters supported the
removal of the current ‘‘yes/no’’
question in section 8.11 of Form R, and
the addition of an optional text box
feature in EPA’s TRI–ME reporting
software. As one commenter stated, TRI
reporters have up until now been forced
to submit additional information about
their source reduction, recycling, and
other pollution prevention techniques
separately on paper, rather than
electronically. The addition of an
electronic text box would allow
facilities to more easily submit such
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information. Another commenter
remarked that such additional
information was not readily accessible
in the past since it was only available
on paper.
EPA agrees with commenters that the
removal of the current question in
section 8.11 and the replacement of it
with an optional electronic text box for
reporting additional information about
source reduction, recycling, and other
pollution prevention techniques will
increase the accessibility and usefulness
of such information. We also believe
that the use of an electronic text box, as
opposed to paper submissions, will
increase the likelihood that reporters
will submit such information since it
will be easier to do so. Accordingly,
EPA has finalized this section of the
proposal.
One commenter did oppose this
change in 8.11, claiming that while the
text box feature is optional, many
reporters will feel compelled to enter
information. The commenter contended
that compliance issues could arise if the
information submitted was not
completely accurate or precise and this
could result in discouraging submission
of such information.
EPA disagrees with this commenter.
Reporters have never been required to
include additional information in
section 8.11, nor would they be required
to do so under this change from paper
to electronic submission. In fact, under
the proposed change, section 8.11
would be entirely optional since those
who do not wish to include additional
information would no longer need to
check the ‘‘no’’ box. Instructions for
using the text box will clearly state that
its use is optional. While EPA does not
believe that compliance issues would
arise from use of the text box, the same
compliance issues triggered by
inaccurate information could have
arisen under the current paper-only
method of submission.
VI. Technical Modifications to 40 CFR
372.85
As discussed in the proposed rule, in
addition to streamlining the TRI
Reporting Forms, EPA also proposed
two technical corrections to 40 CFR
372.85.
Prior to 1991, EPA published the most
current version of the Form R and
Reporting Instructions in its regulations
at 40 CFR 372.85(a). On June 26, 1991,
56 FR 29183, EPA published a final rule
that replaced the full version of the form
and instructions in the regulation with
a Notice of Availability of the most
current version of the Form R and
Reporting Instructions and an address
from which to obtain copies.
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The address for requesting the current
version of Form R is outdated.
Moreover, the likelihood exists that the
address may change from time to time
in the future because the entity
managing Form R distribution may
change. Therefore, EPA is amending 40
CFR section 372.85(a) by giving a
reference to the TRI Web site to obtain
the Form R instead of publishing in the
regulations an address from which to
request copies of TRI forms. EPA is also
providing a phone number from which
to request TRI publications.
EPA received one comment on this
section of the proposal. The commenter
expressed concern that the proposed
change could be misread to imply that
web-based reporting is the only
available reporting option.
This modification should not be
construed to imply that web-based
reporting will be the only reporting
option. This modification simply
updates the method by which a facility
can obtain a copy of the TRI Forms.
After a facility obtains and completes its
form(s), web-based reporting can have
huge potential advantages for both
respondents and the Agency, allowing
respondents to receive pre-populated
forms and the Agency to reduce
processing costs by over 90%. EPA
recognizes, however, that there may be
facilities that do not yet have suitable
internet connectivity. Accordingly, the
modification to section 372.85(a) does
not require reporting by any specific
method.
The 1991 rule also added a list
describing the Form R data elements at
40 CFR 372.85(b). This list includes
Paragraph 18, which describes a
pollution prevention data element. This
data element was optional and set to
expire after the 1990 reporting year.
After the 1991 rule was finalized, EPA
incorporated mandatory pollution
prevention reporting elements pursuant
to the Pollution Prevention Act of 1990.
57 FR 22330. EPA believes the presence
of the outdated Paragraph 18 element in
the regulations is unnecessary since it
has expired. Further, the Agency is
concerned that its continued presence
in the regulations may lead to confusion
about whether pollution prevention data
are required elements of the Form R.
Therefore, EPA is deleting 40 CFR
372.85(b)(18) for the purposes of order
and clarity. This action will not affect
the reporting obligations found in
section 6607 of the PPA; facilities must
continue to report pollution prevention
information as collected in part II,
section 8 of the Form R.
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VII. Regulatory Assessment
Requirements
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order 12866, 58 FR
51735, the Agency must determine
whether this regulatory action is
‘‘significant’’ and therefore subject to
formal review by the Office of
Management and Budget (OMB) and to
the requirements of the Executive Order,
which include assessing the costs and
benefits anticipated as a result of the
proposed regulatory action. The Order
defines ‘‘significant regulatory action’’
as one that is likely to result in a rule
that may: (1) Have an annual effect on
the economy of $100 million or more or
adversely affect in a material way the
economy, a sector of the economy,
productivity, competition, jobs, the
environment, public health or safety, or
state, local, or tribal governments or
communities; (2) create a serious
inconsistency or otherwise interfere
with an action taken or planned by
another agency; (3) materially alter the
budgetary impact of entitlements,
grants, user fees, or loan programs or the
rights and obligations of recipients
thereof; or (4) raise novel legal or policy
issues arising out of legal mandates, the
President’s priorities, or the principles
set forth in the Executive Order.
Pursuant to the terms of Executive
Order 12866, it has been determined
that today’s rule is a significant
regulatory action. The Agency therefore
submitted the proposed action to OMB
for review. Changes made in response to
OMB suggestions or recommendations
are documented in the docket to today’s
final rule.
To estimate the cost savings,
incremental costs, economic impacts
and benefits from this rule to affected
regulated entities, EPA completed an
economic analysis for this rule. Copies
of this analysis (entitled ‘‘Economic
Assessment of the Burden Reduction—
Modifications to Form R—final Rule’’)
have been placed in the TRI docket for
public review.
1. Methodology. To estimate the cost
savings, incremental costs, economic
impacts and benefits of this rule, the
Agency estimated both the cost and
burden of completing the TRI reporting
forms, as well as the number of affected
entities. The Agency used the 2002
reporting year for TRI data as a basis for
these estimates. First, the Agency
identified the number of PBT and nonPBT respondents completing Form R
and non-PBT respondents for Form A
(PBT respondents are currently
ineligible to use Form A). Then the
Agency determined the unit burden
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savings and cost savings per form using
an engineering analysis. Burden savings
for the various forms were calculated
separately because not all final
modifications appear on every form.
The total burden and cost savings
associated with the final modifications
to Forms R and A are the product of the
unit burden and cost savings per form
times the number of forms (Forms R and
A) submitted.
2. Cost & Burden Savings Results.
Table 1 and Table 2 summarize the
number of 2002 first and subsequent
year Forms R and A submissions.
TABLE 1.—NATIONAL BURDEN AND COST SAVINGS FOR FIRST YEAR REPORTERS
Burden
savings per
form R
(hours)
Total burden
savings
(hours)
Cost saving
per form R
Total cost
savings
Number of 2002 forms
Form type
458 ...............................
880 ...............................
324 ...............................
Form R PBT ...........................................................
Form R non-PBT ...................................................
Form A non-PBT ....................................................
2.17
1.37
0.52
996
1,203
168
$97.93
61.99
22.31
$44,852
54,554
7,227
Total .....................
................................................................................
........................
2,367
........................
106,634
TABLE 2.—PRELIMINARY NATIONAL BURDEN AND COST SAVINGS FOR SUBSEQUENT YEAR REPORTERS
Burden
savings per
form R
(hours)
Total burden
savings
(hours)
Cost saving
per form R
Total cost
savings
Number of 2002 forms
Form type
15,085 ..........................
65,006 ..........................
11,594 ..........................
Form R PBT ...........................................................
Form R non-PBT ...................................................
Form A ...................................................................
0.78
0.56
0.11
11,837
36,564
1,292
$33.67
24.73
3.69
$507,856
1,607,661
42,797
Total .....................
................................................................................
........................
49,693
........................
2,158,314
EPA estimates that the total annual
burden savings for this rule are 52,060
hours. EPA estimates that the total
annual cost savings for this rule are
$2.26 million. Average annual cost
savings for facilities submitting Form Rs
or Form As are between $4 and $100 per
form or between $12 and $300 per
facility.
3. Impacts on Data. EPA evaluated the
potential impacts on data from
removing or simplifying these specific
data fields and determined that the risk
of significant data loss is minimal. In
the case of some elements (e.g., latitude
and longitude information), reporting is
being discontinued because information
already exists or can be developed from
other EPA data systems. In other cases
(e.g., changes in waste management or
recycling reporting codes), streamlining
is being proposed to bring reporting
categories in line with existing practices
of other Agency program offices which
should ultimately increase the utility of
the information. Range reporting
options being considered include
intervals selected to maintain relatively
equal population subcategories which
should maintain the utility of the data
while minimizing the potential
uncertainty associated with individual
values. The Agency also conducted
outreach to potentially affected
stakeholders to solicit any specific uses
of the fields being removed or
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simplified. Based on that outreach, the
Agency believes the potential for
significant data loss to the public to be
minimal.
B. Paperwork Reduction Act
We have prepared a document
estimating the recordkeeping and
reporting burden savings associated
with this rule. We calculate the
reporting and recordkeeping burden
reduction for this rule as 52,060 hours
and the estimated cost savings as $2.26
million. Burden means total time, effort,
or financial resources expended by
persons to generate, maintain, retain,
disclose, or provide information to or
for a federal agency. That includes the
time needed to review instructions;
develop, acquire, install, and utilize
technology and systems for the purposes
of collecting, validating, and verifying
information, processing and
maintaining information, and disclosing
and providing information; adjust the
existing ways to comply with any
previously applicable instructions and
requirements; train personnel to be able
to respond to a collection of
information; search data sources;
complete and review the collection of
information; and transmit or otherwise
disclose the information.
C. Regulatory Flexibility Act
The RFA generally requires an agency
to prepare a regulatory flexibility
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analysis of any rule subject to notice
and comment rulemaking requirements
under the Administrative Procedure Act
or any other statute unless the agency
certifies that the rule will not have a
significant economic impact on a
substantial number of small entities.
Small entities include small businesses,
small organizations, and small
governmental jurisdictions.
For purposes of assessing the impacts
of today’s rule on small entities, small
entity is defined as: (1) A small business
that has fewer than either 1000 or 100
employees per firm depending upon the
firm’s primary SIC code; (2) a small
governmental jurisdiction that is a
government of a city, county, town,
school district or special district with a
population of less than 50,000; and (3)
a small organization that is any not-forprofit enterprise which is independently
owned and operated and is not
dominant in its field.
The economic impact analysis
conducted for today’s rule indicates that
these revisions would generally result in
savings to affected entities compared to
baseline requirements. The rule is not
expected to result in a net cost to any
affected entity. Thus, adverse impacts
are not anticipated.
After considering the economic
impacts of today’s rule on small entities,
I certify that this action will not have a
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significant economic impact on a
substantial number of small entities.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), Public
Law 104–4, establishes requirements for
federal agencies to assess the effects of
their regulatory actions on state, local,
and tribal governments and the private
sector. Under section 202 of the UMRA,
EPA generally must prepare a written
statement, including a cost-benefit
analysis, for the proposed and final
rules with ‘‘federal mandates’’ that may
result in expenditures by state, local,
and tribal governments, in the aggregate,
or to the private sector, of $100 million
or more in any one year.
Before promulgating a rule for which
a written statement is needed, section
205 of the UMRA generally requires
EPA to identify and consider a
reasonable number of regulatory
alternatives and adopt the least costly,
most cost-effective or least burdensome
alternative that achieves the objectives
of the rule. The provisions of section
205 do not apply when they are
inconsistent with applicable law.
Moreover, section 205 allows EPA to
adopt an alternative other than the least
costly, most cost-effective, or least
burdensome alternative if the
Administrator publishes with the final
rule an explanation why that alternative
was not adopted.
Before EPA establishes any regulatory
requirements that may significantly or
uniquely affect small governments,
including tribal governments, it must
have developed under section 203 of the
UMRA a small government agency plan.
The plan must provide for notifying
potentially affected small governments,
enabling officials of affected small
governments to have meaningful and
timely input in the development of EPA
regulatory proposals with significant
federal intergovernmental mandates,
and informing, educating, and advising
small governments on compliance with
the regulatory requirements.
The Agency’s analysis of compliance
with the Unfunded Mandates Reform
Act (UMRA) of 1995 found that today’s
rule imposes no enforceable duty on any
state, local or tribal government or the
private sector. This rule contains no
federal mandates (under the regulatory
provisions of Title II of the UMRA) for
state, local, or tribal governments or the
private sector. In addition, EPA has
determined that this rule contains no
regulatory requirements that might
significantly or uniquely affect small
governments. The rule merely
streamlines reporting requirements for
an existing program. Therefore, we have
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14:34 Jul 11, 2005
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determined that today’s rule is not
subject to the requirements of sections
202 and 205 of UMRA.
E. Executive Order 13132: Federalism
Executive Order 13132, entitled
‘‘Federalism’’ 64 FR 43255 (August 10,
1999), requires EPA to develop an
accountable process to ensure
meaningful and timely input by State
and local officials in the development of
regulatory policies that have federalism
implications. ‘‘Policies that have
federalism implications’’ is defined in
the Executive Order to include
regulations that have ‘‘substantial direct
effects on the States, on the relationship
between the national government and
the States, or on the distribution of
power and responsibilities among the
various levels of government.’’ This rule
does not have federalism implications.
It will not have substantial direct effects
on the States, on the relationship
between the national government and
the States, or on the distribution of
power and responsibilities among the
various levels of government, as
specified in Executive Order 13132.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ 65 FR
67249 (November 6, 2000), requires EPA
to develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
implications.’’ ‘‘Policies that have tribal
implications’’ is defined in the
Executive Order to include regulations
that have ‘‘substantial direct effects on
one or more Indian tribes, on the
relationship between the federal
Government and the Indian tribes, or on
the distribution of power and
responsibilities between the federal
government and Indian tribes.’’ This
rule does not have tribal implications. It
will not have substantial direct effects
on tribal governments, on the
relationship between the federal
government and Indian tribes, or on the
distribution of power and
responsibilities between the federal
government and Indian tribes, as
specified in Executive Order 13175.
G. Executive Order 13045: Protection of
Children From Environmental Health &
Safety Risks
‘‘Protection of Children From
Environmental Health Risks and Safety
Risks,’’ 62 FR 19885 (April 23, 1997),
applies to any rule that EPA determines
(1) ‘‘economically significant’’ as
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Fmt 4700
Sfmt 4700
defined under Executive Order 12866,
and (2) concerns an environmental
health or safety risk that EPA has reason
to believe may have a disproportionate
effect on children. If the regulatory
action meets both criteria, the Agency
must evaluate the environmental health
or safety effects of the planned rule on
children and explain why the planned
regulation is preferable to other
potential effective and reasonably
feasible alternatives considered by the
Agency. This rule is not subject to
Executive Order 13045 because it is not
an economically significant rule as
defined by Executive Order 12866.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This rule is not a ‘‘significant energy
action’’ as defined in Executive Order
13211, ‘‘Actions Concerning Regulations
That Significantly Affect Energy Supply,
Distribution, or Use,’’ 66 FR 28355 (May
22, 2001), because it is not likely to have
a significant adverse effect on the
supply, distribution, or use of energy.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law
104–113, section 12(d) (15 U.S.C. 272
note) directs EPA to use voluntary
consensus standards in its regulatory
activities unless to do so would be
inconsistent with applicable law or
otherwise impractical. Voluntary
consensus standards are technical
standards (e.g., materials specifications,
test methods, sampling procedures, and
business practices) that are developed or
adopted by voluntary consensus
standards bodies. The NTTAA directs
EPA to provide Congress, through OMB,
explanations when the Agency decides
not to use available and applicable
voluntary consensus standards. This
rule does not establish technical
standards. Therefore, EPA did not
consider the use of any voluntary
consensus standards.
J. Environmental Justice
Under Executive Order 12898,
‘‘Federal Actions to Address
Environmental Justice in Minority
Populations and Low-Income
Populations’’, EPA has undertaken to
incorporate environmental justice into
its policies and programs. EPA is
committed to addressing environmental
justice concerns, and is assuming a
leadership role in environmental justice
initiatives to enhance environmental
quality for all residents of the United
States. The Agency’s goals are to ensure
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that no segment of the population,
regardless of race, color, national origin,
or income, bears disproportionately
high and adverse human health and
environmental effects as a result of
EPA’s policies, programs, and activities.
EPA has considered the impacts of
this rule on low-income populations
and minority populations and
concluded that it will not cause any
adverse effects to these populations. As
stated above, the Agency has
determined that the risk of significant
data loss is very low. The data elements
being removed or streamlined either
have a low incidence of reporting, have
other data source readily available or do
not appear to be used to any significant
degree by the public.
K. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. EPA will submit a
report containing this rule and other
required information to the U.S. Senate,
the U.S. House of Representatives, and
the Comptroller General of the United
States prior to publication of the rule in
the Federal Register. A Major rule
cannot take effect until 60 days after it
is published in the Federal Register.
This action is not a ‘‘major rule’’ as
defined by 5 U.S.C. 804(2). This rule
will be effective September 12, 2005.
List of Subjects in 40 CFR Part 372
Environmental protection,
Community right-to-know, Reporting
and recordkeeping requirements, Toxic
chemicals.
Dated: June 30, 2005.
Stephen L. Johnson,
Administrator.
iii. Redesignate paragraphs (b)(7)
through (b)(18) as paragraphs (b)(6)
through (b)(17).
I iv. Revise the newly-designated
paragraph (b)(6).
I v. Remove the newly-designated
paragraph (b)(16)(iii).
I vi. Redesignate the newly-designated
paragraphs (b)(16)(iv) and (b)(16)(v) as
paragraphs (b)(16)(iii) and (b)(16)(iv).
I vii. Revise the newly-designated
paragraph (b)(16)(iii).
I viii. Remove the newly-designated
paragraph (b)(17).
I
372.85 Toxic chemical release reporting
form and instructions.
(a) Availability of reporting form and
instructions. The most current version
of Form R may be found on the
following EPA Program Web site,
https://www.epa.gov/tri. Any subsequent
changes to the Form R will be posted on
this Web site. Submitters may also
contact the TRI Program at (202) 564–
9554 to obtain this information.
(b) * * *
(6) Dun and Bradstreet identification
number.
*
*
*
*
*
(16) * * *
(iii) An estimate of the efficiency of
the treatment, which shall be indicated
by a range.
*
*
*
*
*
§ 372.95
[Amended]
3. Section 372.95 is amended as
follows:
I i. Remove paragraphs (b)(11), (b)(13),
(b)(14) and (b)(15).
I ii. Redesignate paragraph (b)(12) as
paragraph (b)(11) and redesignate
paragraphs (b)(16) through (b)(17) as
paragraphs (b)(12) through (b)(13).
I
[FR Doc. 05–13486 Filed 7–11–05; 8:45 am]
BILLING CODE 6560–50–P
DEPARTMENT OF TRANSPORTATION
For the reasons discussed in the
preamble, the Environmental Protection
Agency 40 CFR part 372 is amended as
follows:
I
PART 372—[AMENDED]
Federal Motor Carrier Safety
Administration
49 CFR Part 375
[Docket No. FMCSA–97–2979]
RIN 2126–AA32
1. The authority citation for part 372
continues to read as follows:
I
Authority: 42 U.S.C. 11023 and 11048.
Transportation of Household Goods;
Consumer Protection Regulations;
Final Rule
Subpart E—[Amended]
AGENCY:
2. Section 372.85 is amended as
follows:
I i. Revise paragraph (a).
I ii. Remove paragraph (b)(6).
SUMMARY: The Federal Motor Carrier
Safety Administration (FMCSA) adopts
I
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14:34 Jul 11, 2005
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Federal Motor Carrier Safety
Administration (FMCSA), DOT.
ACTION: Final rule.
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39949
as final its interim regulations at 49 CFR
part 375 published in the Federal
Register on June 11, 2003 (68 FR 35064)
and subsequent technical amendments
published on March 5, 2004 (69 FR
10570), April 2, 2004 (69 FR 17313), and
August 5, 2004 (69 FR 47386). The final
rule specifies how motor carriers
transporting household goods by
commercial motor vehicle in interstate
commerce must assist their individual
customers who ship household goods.
As no further amendments are
necessary, the interim regulations at
part 375 are adopted without change.
DATES: Effective August 11, 2005.
Petitions for Reconsideration must be
received by the agency not later than
August 11, 2005.
FOR FURTHER INFORMATION CONTACT: Ms.
Joy Dunlap, Acting Chief, Commercial
Enforcement Division (MC–ECC), (202)
385–2428, Federal Motor Carrier Safety
Administration, Suite 600, 400 Virginia
Avenue, SW., Washington, DC 20024.
Docket: For access to the docket to
read background documents or
comments received on the interim final
regulations and subsequent
amendments, including a Record of
Meeting and all correspondence
referenced in this document, go to
https://dms.dot.gov at any time or to
Room PL–401 on the Plaza level of the
Nassif Building, 400 Seventh Street,
SW., Washington, DC, between 9 a.m.
and 5 p.m., Monday through Friday,
except Federal Holidays.
Privacy Act: Anyone is able to search
the electronic form of all comments
received into any of DOT’s dockets by
the name of the individual submitting
the comment (or signing the comment,
if submitted on behalf of an association,
business, labor union, etc.). You may
review DOT’s complete Privacy Act
Statement in the Federal Register
published on April 11, 2000 (65 FR
19477). This statement is also available
at https://dms.dot.gov.
SUPPLEMENTARY INFORMATION:
Legal Basis for the Rulemaking
The Interstate Commerce Commission
Termination Act of 1995 (ICCTA) (Pub.
L. 104–88, 109 Stat. 803) provides that
‘‘[t]he Secretary may issue regulations,
including regulations protecting
individual shippers, in order to carry
out this part with respect to the
transportation of household goods by
motor carriers subject to jurisdiction
under subchapter 1 of chapter 135. The
regulations and paperwork required of
motor carriers providing transportation
of household goods shall be minimized
to the maximum extent feasible
consistent with the protection of
E:\FR\FM\12JYR1.SGM
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Agencies
[Federal Register Volume 70, Number 132 (Tuesday, July 12, 2005)]
[Rules and Regulations]
[Pages 39931-39949]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 05-13486]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 372
[TRI-2004-0001; FRL-7532-6]
RIN 2025-AA15
Toxics Release Inventory Reporting Forms Modification Rule
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: To improve reporting efficiency and effectiveness, reduce
burden, and promote data reliability and consistency across Agency
programs, EPA is simplifying the Toxics Release Inventory (TRI)
reporting requirements. TRI reporting is required by section 313 of the
Emergency Planning and Community Right-to-Know Act (EPCRA) and section
6607 of the Pollution Prevention Act (PPA). This rule simplifies the
TRI reporting requirements by removing some data elements from the Form
R and Form A Certification Statement (hereafter referred to as Form A)
that can be obtained from other EPA information collection databases,
streamlining other TRI data elements through range codes and a reduced
number of reporting codes, and eliminating a few data elements from the
Form R. This rule also makes two technical corrections to the
regulations to provide corrected contact information and to remove an
outdated description of a pollution prevention data element.
DATES: This rule is effective on September 12, 2005. The first reports
with the revised reporting requirements will be due on or before July
1, 2006, for reporting year (i.e., calendar year) 2005.
ADDRESSES: EPA has established a docket for this action under Docket ID
No. TRI-2004-0001. All documents in the docket are listed in the
EDOCKET index at https://www.epa.gov/edocket. Although listed in the
index, some information is not publicly available, i.e., CBI or other
information whose disclosure is restricted by statute. Certain other
material, such as copyrighted material, is not placed on the Internet
and will be publicly available only in hard copy form. Publicly
available docket materials are available either electronically in
EDOCKET or in hard copy at the OEI Docket, EPA/DC, EPA West, Room B102,
1301 Constitution Ave., NW., Washington, DC. The Public Reading Room is
open from 8:30 a.m. to 4:30 p.m., Monday through Friday, excluding
legal holidays. The telephone number for the Public Reading Room is
(202) 566-1744, and the telephone number for the OEI Docket is (202)
566-1752.
FOR FURTHER INFORMATION CONTACT: Shelley Fudge, Toxics Release
Inventory Program Division, Office of Information Analysis and Access
(2844T), Environmental Protection Agency, 1200 Pennsylvania Ave., NW.,
Washington, DC 20460; telephone number: (202) 566-0674; fax number:
(202) 566-0741; e-mail address: fudge.shelley@epa.gov for specific
information on this proposed rule. For more information on EPCRA
section 313, contact the TRI Information Center, Toll free: (800) 424-
9346, TDD: (800) 553-7672, callers in the DC area: (703) 412-9810.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does This Action Apply to Me?
This document applies to facilities that submit annual reports
under section 313 of the Emergency Planning and Community Right-to-Know
Act (EPCRA). It specifically applies to those who submit the TRI Form R
or Form A. (See https://epa.gov/tri/report/index.htm#forms for detailed
information about EPA's TRI reporting forms.) To determine whether your
facility is affected by this action, you should carefully examine the
applicability criteria in part 372 subpart B of Title 40 of the Code of
Federal Regulations. If you have questions regarding the applicability
of this action to a particular entity, consult the person listed in the
preceding FOR FURTHER INFORMATION CONTACT section.
This document is also relevant to those who utilize EPA's TRI
information, including State agencies, local governments, communities,
environmental groups and other non-governmental organizations, as well
as members of the general public.
II. What Is EPA's Statutory Authority for Taking These Actions?
This rule is being issued under sections 313(g)(1) and 328 of
EPCRA, 42 U.S.C. 11023(g)(1) and 11048; and section 6607(b) of the
Pollution Prevention Act (PPA), 42 U.S.C. 13106. In general, section
313 of EPCRA and section 6607 of PPA require owners and operators of
facilities in specified SIC codes that manufacture, process, or
otherwise use a listed toxic chemical in amounts above specified
threshold levels to report certain facility-specific information about
such chemicals, including the annual releases and other waste
management quantities. Section 313(g)(1) of EPCRA requires EPA to
publish a uniform toxic chemical
[[Page 39932]]
release form for these reporting purposes, and it also prescribes, in
general terms, the types of information that must be submitted on the
form. In addition, Congress granted EPA broad rulemaking authority to
allow the Agency to fully implement the statute. EPCRA section 328
authorizes the ``Administrator [to] prescribe such regulations as may
be necessary to carry out this chapter.'' 42 U.S.C. 11048.
III. What Is the Background and Purpose of Today's Actions?
A. What Are the Toxics Release Inventory Reporting Requirements and Who
Do They Affect?
Pursuant to section 313(a) of the Emergency Planning and Community
Right-to-Know Act (EPCRA), certain facilities that manufacture,
process, or otherwise use specified toxic chemicals in amounts above
reporting threshold levels must submit annually to EPA and to
designated State officials toxic chemical release reporting forms
containing information specified by EPA. 42 U.S.C. 11023(a). These
reports must be filed by July 1 of each year for the previous calendar
year. In addition, pursuant to section 6607 of the Pollution Prevention
Act (PPA), facilities reporting under section 313 of EPCRA must also
report pollution prevention and waste management data, including
recycling information, for such chemicals. 42 U.S.C. 13106. These
reports are compiled and stored in EPA's database known as the Toxics
Release Inventory (TRI).
The statute, along with regulations at 40 CFR part 372, subpart B,
requires facilities that meet all of the following criteria to report:
The facility has 10 or more full-time employee equivalents
(i.e., a total of 20,000 hours worked per year or greater; see 40 CFR
372.3); and
The facility is included in Standard Industrial
Classification (SIC) Codes 10 (except 1011, 1081, and 1094), 12 (except
1241), 20-39, 4911 (limited to facilities that combust coal and/or oil
for the purpose of generating electricity for distribution in
commerce), 4931 (limited to facilities that combust coal and/or oil for
the purpose of generating electricity for distribution in commerce),
4939 (limited to facilities that combust coal and/or oil for the
purpose of generating electricity for distribution in commerce), 4953
(limited to facilities regulated under Resource Conservation Recovery
Act (RCRA) Subtitle C, 42 U.S.C. 6921 et seq.), 5169, 5171, and 7389
(limited to facilities primarily engaged in solvents recovery services
on a contract or fee basis), or, under Executive Order 13148, federal
facilities regardless of their SIC code; and
The facility manufactures (defined to include importing),
processes, or otherwise uses any EPCRA section 313 (TRI) chemical in
quantities greater than the established threshold for the specific
chemical in the course of a calendar year.
Facilities that meet the criteria must file a Form R report or in
some cases, may submit a Form A Certification Statement for each listed
toxic chemical for which the criteria are met. As specified in EPCRA
section 313(a), the report for any calendar year must be submitted on
or before July 1 of the following year. For example, reporting year
2003 data should have been postmarked on or before July 1, 2004.
The list of toxic chemicals subject to TRI can be found at 40 CFR
372.65. This list is also published every year as Table II in the
current version of the Toxic Chemical Release Inventory Reporting Forms
and Instructions. The current TRI chemical list contains 582
individually-listed chemicals and 30 chemical categories.
B. Why Are We Modifying the Form A Certification Statement and Form R?
EPA is modifying the TRI reporting forms to improve efficiency and
effectiveness, reduce burden, and promote data reliability and
consistency across Agency programs.
One of the purposes of today's actions is to reduce burden on
facilities that submit annual TRI reports without compromising the data
quality of toxic chemical release and other waste management
information. ``Burden'' is the total time, effort, or financial
resources expended by persons to generate, maintain, retain, disclose,
or provide information to or for a federal agency. 44 U.S.C. 3502(2).
That includes the time needed to review instructions; develop, acquire,
install, and utilize technology and systems for the purposes of
collecting, validating, and verifying information, processing and
maintaining information, and disclosing and providing information;
adjust the existing ways to comply with any previously applicable
instructions and requirements; train personnel to be able to respond to
a collection of information; search data sources; complete and review
the collection of information; and transmit or otherwise disclose the
information.
EPA has made considerable progress in reducing burden associated
with its various information collections through streamlining,
consolidating and harmonizing regulations, guidance and compliance
assistance, and implementing technology-based processes (i.e.,
electronic reporting, cross program data utilization, using geospatial
information to pre-populate data fields). These measures have reduced
the time, cost, and complexity of existing environmental reporting
requirements, while enhancing reporting effectiveness and efficiency.
Today's actions reduce the time, cost and complexity of the
reporting requirements imposed on facilities. While they are only
expected to result in a modest amount of cost and burden savings, they
also represent only the first phase of a broader and more substantive
set of regulatory burden reduction alternatives currently being
examined by EPA. That effort, described in more detail below, is
expected to provide additional regulatory relief for TRI reporters.
A second purpose of today's rule is to improve data reliability and
consistency across EPA programs. By replacing self-reported data from
facilities with data from EPA's Facility Registry System on items such
as latitude and longitude and facility ID numbers for other EPA
programs, EPA can better ensure that this information is reported
consistently across programs and facilities. Further, as locational
information will have method of collection, accuracy, and a description
of the location to which the coordinates correspond (e.g., production
center, discharge point), data users will be able to utilize
information with greater confidence. By streamlining reporting
requirements and improving data reliability and consistency, this rule
will improve reporting efficiency and effectiveness.
C. What Led to the Development of This Rule?
Throughout the history of the TRI program the Agency has
implemented measures to improve reporting efficiency and effectiveness
and reduce the TRI reporting burden on the regulated community. Through
a range of compliance assistance activities, such as the Toxic Chemical
Release Inventory Reporting Forms & Instructions (which is published
and mailed every year), industry training workshops, chemical-specific
and industry-specific guidance documents, and the EPCRA Call Center (a
call hotline), the Agency has shown a commitment to enhancing the
quality and consistency of reporting, and assisting those facilities
that must comply with EPCRA section 313.
EPA has also done extensive work to make reporting easier for the
TRI reporting community through the development and use of technology,
[[Page 39933]]
such as EPA's Toxics Release Inventory--Made Easy software, otherwise
known as ``TRI-ME'' (https://www.epa.gov/tri/report/trime/). TRI-ME is
an interactive, user-friendly software tool that guides facilities
through the TRI reporting process. By leading prospective reporters
through a series of logically-ordered questions, TRI-ME facilitates the
analysis needed to determine if a facility must complete a Form R or A
report for a particular chemical. For those facilities required to
report, the software provides guidance for each data element on Forms R
and A. TRI-ME has a one-stop guidance feature, the TRI Assistance
Library, which allows keyword searches on the statutes, regulations,
and many EPCRA section 313 guidance documents. TRI-ME also offers a
``load feature'' that enables the user to upload almost all of the
facility's prior year data into the current year's report. Finally,
TRI-ME checks the data for common errors and then prepares the forms to
be sent electronically over the Internet via EPA's Central Data
Exchange (CDX). TRI-ME generated reporting forms may also be submitted
offline via magnetic media or on paper. In the spring of 2005, EPA
distributed approximately 5,000 copies of TRI-ME in preparation for the
2004 reporting year deadline of July 1, 2005. Approximately 93% of the
roughly 98,000 Form Rs filed in 2004 were prepared using the TRI-ME
software.
In 1994, partially in response to petitions received from the U.S.
Small Business Administration Office of Advocacy and the American Feed
Industry Association, an EPA rulemaking established the Form A
Certification Statement as an alternative to Form R. This burden-
reducing measure was based on an alternate threshold for quantities
manufactured, processed, or otherwise used by those facilities with
relatively low annual reportable amounts of TRI chemicals. For non-PBT
chemicals, a facility may use the Form A if the facility manufactures,
processes or otherwise uses a TRI chemical below the alternate
threshold of one million pounds per year and the facility has annual
reportable amounts of these toxic chemicals not exceeding 500 pounds.
The annual reportable amount is the total of the quantity released at
the facility, the quantity treated at the facility, the quantity
recovered at the facility as a result of recycle operations, the
quantity combusted for the purpose of energy recovery at the facility,
and the quantity transferred off-site for recycling, energy recovery,
treatment, and/or disposal. This combined total corresponds to the
quantity of the toxic chemicals in production-related waste (i.e., the
sum of sections 8.1 through and including section 8.7 on the Form R).
In an effort to further explore burden reduction opportunities, EPA
conducted a TRI Stakeholder Dialogue between November 2002 and February
2004. The dialogue process focused on identifying improvements to the
TRI reporting process and exploring a number of burden reduction
options associated with TRI reporting. In total, EPA received
approximately 770 documents as part of this stakeholder dialogue. Of
that, approximately 730 were public comments and the remaining
documents were either duplicates or correspondence transmitting public
comments to the online docket system. The public comments expressed a
range of views, with some supporting burden reduction and others
opposing it. You may view and obtain copies of all documents submitted
to EPA by accessing TRI docket TRI-2003-0001 online at https://
www.epa.gov/edocket or by visiting the EPA docket reading room in
Washington, DC.
As a result of the Stakeholder Dialogue, the Agency identified a
number of burden reducing options which will continue to support
existing data uses and statutory and regulatory obligations. These
changes fall into two broad categories: (1) Changes or modifications to
the reporting forms and processes (including modifications to the forms
and improvements in the TRI-ME software) which will streamline
reporting without significantly affecting the information collected;
and (2) what the Agency believes are more substantial changes that may
affect which facilities are required to report and at what level of
detail.
EPA decided to address the two categories of changes through
separate rulemakings, one of which is today's action. This rule focuses
on streamlining reporting associated with TRI's Forms R and A. The
changes resulting from today's action are the elimination of some
redundant or seldom-used data elements from these forms, and
modification of other data elements to reduce the time and costs
required to complete and submit annual TRI reports. It also replaces
some elements with information from EPA's Facility Registry System in
order to improve data reliability and consistency. EPA is confident
these changes will enhance the efficiency and effectiveness of the TRI
program by reducing reporting requirements, while continuing to provide
communities and other data users with the same, or higher quality,
chemical release and other waste management information.
The second rulemaking, to be proposed later in 2005, will examine
the potential for more significant reporting modifications with greater
potential impact on reducing reporting burden. The options which may be
considered in that rulemaking include expanding eligibility for Form A
and introducing a ``no significant change'' option for chemical reports
that have not changed significantly relative to a baseline reporting
year. Because of the greater complexity and larger impacts potentially
associated with this latter group of changes, additional analysis is
needed to more thoroughly characterize its impact on TRI reporters and
data users.
IV. Summary of Today's Final Rule
EPA is removing from the TRI Forms R and A the latitude/longitude
data elements (section 4.6, Part I), the EPA Identification Number(s)
(RCRA ID No.) (section 4.8, Part I), the Facility NPDES Permit
Number(s) (section 4.9, Part I), and the Underground Injection Well
Code (UIC) ID Number(s) (section 4.10, Part I). Instead of continuing
to request this information from the TRI reporter, the Agency's
Facility Registry System (FRS) will be used to populate the TRI
database with this information. This information will continue to be
made readily available for all TRI reports and applications such as the
publicly accessible TRI Explorer and all Form A or R retrievals from
Envirofacts at https://www.epa.gov/enviro/index_java.html. In other
words, facility identification and locational data will still be made
available for all reporters and data users, but instead of requiring
facilities to supply their geographic coordinates or provide certain
EPA program identification and permit numbers, the Agency will extract
this data from information that is already collected, stored and
maintained in its centrally managed database, the FRS.
Based on comments received and information gathered since the
proposed rule, EPA is not removing from Form R or modifying in any way,
part II, section 5.3 column C as part of today's rule. Section 5.3
applies to discharges to receiving streams and water bodies. Column C
requires facilities to indicate the percentage of the total quantity of
the EPCRA section 313 chemicals reported in column A (Total release)
that are discharged from stormwater.
As part of today's action, the Agency is, however, making
modifications to five data elements of part II, section 7 of the Form
R. This rule simplifies column B of section 7A--Waste
[[Page 39934]]
Treatment Method(s) Sequence, by replacing 64 codes used to describe
the various waste treatment methods applied to EPCRA section 313
chemicals treated on-site with a modified version of the 18 hazardous
waste treatment codes (H040-H129), as they were described in the
proposed rule. These 18 codes are a modified version of the codes used
in EPA's National Biennial Resource Conservation Recovery Act (RCRA)
Hazardous Waste Report (hereafter referred to as the RCRA Biennial
Report). (See PDF screen page 63 of the 2003 Hazardous Waste Report
Instructions and Forms (booklet) [EPA Form 8700-13 A/B; 11/2000]
available at https://www.epa.gov/epaoswer/hazwaste/data/br03/
03report.pdf). Based on comments submitted, several modifications were
made to the list of H codes presented in the proposed rule. For
example, in the proposed rule EPA inadvertently omitted treatment code
H083 (Air or steam stripping) from the list of 18 hazardous waste
treatment codes. This was an oversight and EPA has included this code
in today's rule. Furthermore, ``as the major component of treatment''
has been removed as a qualifier from H082 (Adsorption as the major
component of treatment) and H083 (Air or steam stripping as the major
component of treatment), ``at another site'' has been removed as a
qualifier from H111 (Stabilization or chemical fixation prior to
disposal at another site) and H112 (Macro-encapsulation prior to
disposal at another site), and ``only'' has been removed as a qualifier
from H121 (Neutralization only).
In addition, based on comment received on the proposed modification
to section 7A column B, EPA has decided to retain the seven Air
Emissions Treatment codes currently available for reporting in column B
(see page 55 of the 2004 TRI Reporting Forms and Instructions (EPA 260-
B-05-001, January 2005) at https://epa.gov/tri/report/index.htm#forms).
Accordingly, this rule finalizes the following list of waste treatment
codes for reporting in part II, section 7A, column B of Form R:
A01 Flare
A02 Condenser
A03 Scrubber
A04 Absorber
A05 Electrostatic Precipitator
A06 Mechanical Separation
A07 Other Air Emission Treatment
H040 Incineration--thermal destruction other than use as a fuel
H071 Chemical reduction with or without precipitation
H073 Cyanide destruction with or without precipitation
H075 Chemical oxidation
H076 Wet air oxidation
H077 Other chemical precipitation with or without pre-treatment
H081 Biological treatment with or without precipitation
H082 Adsorption
H083 Air or steam stripping
H101 Sludge treatment and/or dewatering
H103 Absorption
H111 Stabilization or chemical fixation prior to disposal
H112 Macro-encapsulation prior to disposal
H121 Neutralization
H122 Evaporation
H123 Settling or clarification
H124 Phase separation
H129 Other treatment
This rule eliminates section 7A, column C--Range of Influent
Concentration from the Form R.
Today's action allows facilities to report their treatment
efficiency as a range instead of an exact percentage in column D (Waste
Treatment Efficiency Estimate) of section 7A of Form R using the
following ranges:
E1 = greater than 99.9999%
E2 = greater than 99.99%, but less than or equal to 99.9999%
E3 = greater than 99%, but less than or equal to 99.99%
E4 = greater than 95%, but less than or equal to 99%
E5 = greater than 50%, but less than or equal to 95%
E6 = equal to or greater than 0% but less than or equal to 50%
This set of ranges is different from the set of ranges proposed.
The ranges were modified from the proposal to allow data users to
continue to distinguish the performance of combustion devices in excess
of RCRA hazardous waste and TSCA PCB incinerator standards. The mid and
lower range treatment efficiencies were modified as well, in response
to comments to reduce the number of categories in those ranges and
better reflect the distribution of historical values.
This rule eliminates column E (Based on Operating Data) of section
7A from Form R.
This rule also removes the current recycling codes for section 7C
(On-Site Recycling Processes) of the Form R and replaces them with the
following three reclamation and recovery management categories used in
EPA's RCRA Biennial Report:
H10 Metal recovery (by retorting, smelting, or chemical or physical
extraction)
H20 Solvent recovery (including distillation, evaporation,
fractionation or extraction)
H39 Other recovery or reclamation for reuse (including acid
regeneration or other chemical reaction process)
See the PDF screen page 63 of the 2003 Hazardous Waste Report
Instructions and Forms (booklet) (EPA Form 8700-13 A/B; 11/2000)
available at https://www.epa.gov/epaoswer/hazwaste/data/br03/
03report.pdf. Readers will note that the actual code numbers differ
slightly from those in the RCRA instructions in that the leading ``0''
(i.e., H020 ) has been removed from each code name. This was done to
avoid the need to reprogram TRI-ME, thus saving administrative costs.
The Agency does not believe this will cause any confusion.
Today's action also modifies section 8.11 of Form R by removing the
requirement to answer ``yes'' or ``no'' to this optional section on
additional information on source reduction, recycling, or pollution
control activities. Instead, an optional question will replace the
requirement to answer ``yes'' or ``no'' and an optional text box
feature will be added to EPA's TRI-ME reporting software to enable
reporting facilities to add a brief description of their applicable
source reduction, recycling, and other pollution control techniques and
activities. Facilities will still have the opportunity to submit hard
copies of any source reduction information they may wish to submit.
Finally, through this rule EPA is amending 40 CFR 372.85(a) to
provide a reference to the TRI Web site to obtain the Form R instead of
publishing in the regulations an incorrect physical address from which
to request copies of TRI forms. In addition, EPA will also provide a
phone number from which to request TRI publications. EPA is also
deleting 40 CFR 372.85(b)(18), an outdated pollution prevention data
element, which expired after the 1990 reporting year.
V. Summary of Public Comments and EPA Responses
EPA received 31 distinctive comments in response to this proposed
rule. While the majority of commenters were supportive of today's
actions, many commenters cautioned the Agency to make sure that the
changes do not result in diminished data quality, utility, or
accessibility. Some commenters urged the Agency to consider data user
needs and to balance user needs with burden reduction. A number of
commenters also stated that today's actions will only provide minimal
burden relief, especially since some of the changes are for information
that is collected by the facility one time and used from year-to-year.
Others
[[Page 39935]]
expressed concerns about the initial transaction costs that TRI
reporters, as well as the states, may incur to account for these
reporting changes and to modify training materials and analysis
mechanisms already in place.
The TRI reporting form changes in today's rule support existing
data uses and fulfill statutory and regulatory obligations. They are
the first step in the Agency's larger effort to reduce reporting burden
for TRI reporters while at the same time, these changes allow the
Agency to continue to provide valuable information to the public
consistent with the goals and statutory requirements of the TRI
program. Some of the changes being finalized today will shift the
burden to the Agency, and will increase the quality of locational data
and EPA program identification information (also referred to
collectively hereafter as facility identification information). Other
changes being finalized today will reduce computational burden, but
maintain the availability of information in a form commensurate with
its true underlying precision. Accordingly, EPA does not believe there
will be a meaningful loss of information for users.
While today's changes provide only a modest amount of burden
relief, they are important nonetheless, and based on comments received,
many TRI reporters support this burden relief measure. EPA is committed
to all of its ongoing burden reduction activities. As stated in the
proposed rule and above at Unit III.C., the Agency is pursuing a
broader and more substantive set of regulatory burden reduction
alternatives in a future rulemaking.
EPA acknowledges that changes to the TRI reporting forms could lead
to some initial transition costs for TRI reporting facilities and other
TRI stakeholders. Balanced against this consideration, of course, is
the fact that these changes will remove certain data elements from the
reporting forms and simplify others, thereby making it easier for
industry to comply with the TRI reporting requirements after the
changes are made. For example, whereas Form R previously required
reporters to distinguish between three separate on-site wastewater
treatment method codes for cyanide oxidation, the changes finalized
today will allow reporters to use one cyanide oxidation treatment code.
In addition, the initial burden from adjusting to the form
modifications that the commenters predict will not affect new
reporters.
Further, EPA's TRI-ME software can be used by reporters to greatly
ease reporting burden. The software guides reporters through a series
of logically ordered questions that helps them determine how to meet
their regulatory obligations, and provides various tools for completing
the reporting forms. The changes finalized in today's rule will be
incorporated into the TRI-ME software. EPA does not require facilities
or others to develop additional data collection, tracking or other
databases or documentation. Neither does the Agency require any special
training materials or courses as a result of today's actions.
EPA does not believe that this rule will impose significant burden
on the states. Most of the changes being finalized are in the form of
eliminating data elements. The Agency will continue to make all
facility identification data available through the Facility Registry
System (FRS). Furthermore, the Agency will continue to work with the
states to improve electronic information exchange capability and the
timeliness of such exchanges.
EPA's National Environmental Information Exchange Network
(``Exchange Network'') provides state partners the capability to access
data through a streamlined web services process. As more states
participate, they will be provided with the ability to use the Exchange
Network's built-in quality checks, standard file formats, and a common,
user-friendly approach to exchanging data. A majority of states already
take advantage of EPA's Exchange Network. In addition, we expect
numerous benefits to result from the centralization of data in the
Agency's FRS, which provides an integrated, comprehensive source of
information about facilities subject to a variety of environmental
statutes and regulations. As an essential part of implementing this
rule, EPA will provide increased access to both the FRS resources and
the Agency's Integrated Error Correction Process (IECP), so that
states, facilities, and the general public can more easily access
facility identification information and report data errors when
appropriate.
Finally, some commenters raised issues about burden reduction
(e.g., no significant change certification criteria, expanded
eligibility for Form A) that will be addressed in another rulemaking
(discussed above in Unit III.C.) to be proposed later this year. Other
commenters raised issues unrelated to this rulemaking (e.g., providing
additional context for the TRI data). These comments are included in
the public docket for this rulemaking but will not be addressed in this
rule.
A. Replacement of Certain Facility Identification Data Reporting
Requirements (Sections 4.6 and 4.8 Through 4.10 of Forms R and A) With
Existing EPA Data From the EPA Facility Data Registry
In the proposed rule, EPA requested comment on removing reporting
of certain facility identification data (latitude/longitude coordinates
and certain EPA program and permit identification numbers) from the TRI
forms. Instead of collecting the data annually from facilities, EPA
would use the centralized EPA database, known as the Facility Registry
System (FRS), to populate the TRI database with this information.
Specifically, EPA proposed populating the TRI database with latitude
and longitude information (also referred to as locational data or
locational information) from the FRS.
Under this proposal, locational information from FRS, including a
description of what the latitude and longitude coordinates represent
(e.g., center of production, pipe outfall, stack) would be made readily
available for all TRI search applications, such as the publicly
accessible TRI Explorer and all Form R and A retrievals from
Envirofacts. Similarly, as part of the proposed rule, EPA requested
comment on automatically populating the TRI database with EPA program
and permit identification numbers (except the TRI facility
identification number (TRIFID), which facilities must continue to
report annually), from FRS as an alternative to requesting the
information from TRI reporters. The program and permit identification
numbers that will be populated from FRS include the numbers assigned to
facilities under the Resource Conservation and Recovery Act (RCRA), the
permit identification numbers under the National Pollutant Discharge
Elimination System (NPDES), and the permit numbers issued by a state to
facilities with underground injection control wells (UIC).
As discussed in the proposed rule, the FRS is a centrally-managed
database developed by EPA's Office of Environmental Information (OEI).
FRS provides Internet access to a single source of comprehensive
information about facilities that are subject to environmental
regulations and/or have attributes that are of environmental interest
to EPA. The FRS database currently contains over 1.5 million unique
facility records, and new facilities are continuously being added to
the system, either through information supplied by EPA programs or
through our state partners on the Exchange Network. At this time,
facility
[[Page 39936]]
identification data are exchanged with over three dozen states through
the Exchange Network. FRS also receives correction and verification
information from the reporting community through Web-based access, and
through EPA database systems, such as TRI, maintained by over a dozen
EPA programs.
Eight commenters supported removing the proposed facility
identification data from Forms R and A, and instead, replacing these
data elements with data from the Agency's FRS so that TRI reporters
would no longer have to annually report these data elements on their
Form Rs or As. Several commenters voiced support for greater
consistency between EPA's program databases, as well as increased
simplification and standardization of the facility identification data
that EPA collects, stores and makes available to the public. One
commenter asserted that this change would enhance TRI reporting
efficiency and improve data quality, especially if existing databases
are utilized for populating Forms R and A. Two commenters stated that
these changes would ease paperwork and reporting burdens and lead to
greater consistency on data collection across Agency programs. Several
commenters stated that the change would help eliminate redundant data
collection. One commenter stated that the change would promote wider
use of the FRS. Another commenter asserted that the change should help
avoid data entry errors and promote consistent reporting of facility
locational data.
EPA agrees with the commenters that the Agency's databases should
be standardized and made consistent as much as possible across various
programs. This regulatory change is part of a larger Agency initiative
to increase the reliability and accuracy of the Agency's FRS database
system. Accordingly, EPA is finalizing its proposal to use FRS to
supply the data for sections 4.6 and 4.8 through 4.10 of Forms R and A.
Before finalizing this proposal, however, EPA evaluated the
concerns expressed about ``inherent flaws'' in the Agency's FRS that
compromise the Agency's efforts to consolidate environmental data,
minimize reporting redundancies and create a single identification
system. Contrary to statements in the proposed rule, one commenter
claimed that facility identification records in FRS are not accurate or
authoritative. A commenter asserted that this understanding is
supported by industry representatives who must reconcile FRS data with
company records. A number of commenters emphasized that it was
imperative to enable the public to easily retrieve all environmental
information about a specific facility.
Commenters did not provide data to substantiate their claims of
erroneous information in FRS. Nevertheless, the Agency examined FRS
coverage of EPA program identifiers in the context of RCRA
identification numbers (hereafter referred to as RCRA IDs) to test the
commenters' concern. The FRS database contains all EPA program
identification numbers that are stored in EPA's national program system
databases. Regarding RCRA, FRS contains all the RCRA IDs from the
RCRAInfo database, and is thus a definitive source for such
information. The Agency examined over 10,000 TRI forms with RCRA IDs
from the 2002 reporting year. A description of this study is included
below under Unit V.A.2. of this preamble.
It is important to note here that the FRS database covers all the
TRI reports for reporting year 2003 and has retained all TRIFIDs (there
are over 49,000 of them) since the TRI program began in the late 1980s.
FRS also has the latitude and longitude coordinates for all historical
TRIFIDs. The Burden Reduction Rule will not impair the public's access
to information about TRI reporting facilities, including locational
data and EPA program identification numbers. These data will continue
to be publicly available through various TRI access tools. Only now
they will be supplied by the larger and more authoritative data files
in FRS. To the extent that inconsistencies and errors are identified in
the future, the Agency's Integrated Error Correction Process (IECP)
will provide a convenient and effective mechanism for bringing these
issues to the Agency's attention for resolution.
Two commenters asserted that ideally, EPA should refrain from
relying on FRS to supply data to TRI until all states are participating
in the Exchange Network and have the capability to upload data into
FRS. One commenter stated that 14 states are still not active in the
Exchange Network. The commenter asserted that data regarding facilities
in non-participating Exchange Network states are not being scrutinized
by people most familiar with those facilities. According to the
commenter, until all states are part of the network, EPA lacks the
``on-the-ground'' intelligence needed to ensure that FRS data is
accurate or complete.
EPA agrees that ideally all the states should be part of the
existing Exchange Network. However, we believe that the commenter that
urged EPA to wait to implement this rule ``until all states are
participating in the FRS program'' may not have understood that FRS
contains data about regulated facilities' identification information
that has been provided both by EPA's many database systems and by many
state environmental agencies. States do not need to take any specific
action to access information data from FRS and information is available
in FRS for facilities in states that aren't yet a part of the Exchange
Network from various EPA sources. Anyone, including state agencies, can
access data from FRS at any time. While it is true that not all states
currently participate in the Exchange Network, the vast majority of
states do participate, and EPA is working closely with non-
participating states to help facilitate their full participation in the
near future.
Accordingly, EPA does not agree that the rule should be delayed
until all states are participating in the Exchange Network, nor does
EPA agree that the Agency lacks the ``on-the-ground'' intelligence
needed to ensure that FRS data are accurate or complete until such
time. The FRS is already functioning and will be further enhanced as
part of the effort to implement this rule. EPA will provide all states
and other data users the opportunity to correct inaccurate TRI data.
All states and reporters will be able to correct inaccurate information
on locational data and EPA program identification numbers through the
Agency's Integrated Error Correction Process (IECP). As explained in
the proposed rule, another advantage of utilizing information in the
FRS is that one can take advantage of EPA's Public Internet site to
submit corrections to EPA's data on regulated facilities through one
central access point. The IECP unifies the process by which EPA
regulatory programs manage error notifications to the data in their
systems. IECP is part of an ongoing EPA effort to improve the quality
of EPA's publicly available data. Through the IECP, the public can
directly notify EPA of a data error they've identified in EPA's
publicly available data. They may notify EPA through a variety of
venues that include the following: (1) Selecting the ``Contact Us''
hotlink from the EPA Home Page and accessing the link ``report data
errors'', (2) calling the IECP desk, (3) sending a fax, or (4) e-
mailing a detailed description of the error.
Furthermore, the Agency will take one additional step to ensure a
smooth transition to the use of FRS. For reporting year 2004, the e-FDR
is expected to be publicly released in the fall of 2005. At the time of
the posting of the individual TRI reporting form
[[Page 39937]]
submissions (which will still contain the collected facility
identification data elements), EPA will also post the facility
identification information stored in FRS. This will enable interested
parties to directly observe the data and confirm its accuracy. Lastly,
the Agency will be working closely with all states to ensure a smooth
transition to the utilization of pre-existing facility identification
data in FRS.
One commenter recommended that EPA delay implementing the use of
FRS to supply facility locational data and EPA program identification
numbers until a pilot study is conducted to ensure that these data are
of equal or higher quality in FRS than the data which are contained in
the TRI database. In addition, according to the commenter, problems
arise when the TRI dataset contains locational data for facilities that
FRS does not cover. While having all states as part of the Exchange
Network may help address these problems, the commenter asserted that
there are inherent limits to this kind of after-the-fact
reconciliation. The commenter urged EPA to delay implementation until
the FRS dataset is complete and the agency can ensure the accuracy of
the data.
While EPA does not agree that we should delay using FRS to access
TRI facility identification information until a pilot study can be
undertaken, a separate assessment was conducted of locational
information in FRS versus that contained in the TRI database. The
locational information in the two systems was compared on the basis of
performance against two criteria: A quality screening approach and
conformance to the Agency's data standards for locational information.
Absent very detailed site information, it is difficult to design a
locational screening test. What the Agency did was to compare the
locational data stored in FRS versus such data in the TRI database on a
county basis (i.e., what percentage of reported locational data were
within the boundaries of the counties where the facilities' street
addresses were located). While it is possible for a street address to
vary appreciably from the location of the facility's center of
production, the Agency believes this test provides a first
approximation of relative performance. We found that 98% of all FRS
locational data as opposed to 97% of all TRI locational data met this
criterion. Therefore, on the basis of this broad measure, the two
systems had comparable information.
For the second test, the Agency looked at how the data conformed
with the Agency's data standards for locational information (i.e., a
description of the method of data collection and what is measured, as
well as probable accuracy). Fully 89% of all TRI facility locational
data for reporting year 2003 would have been able to meet the Agency's
data standard requirements if FRS had been used to derive TRI
locational data. Currently, none of the TRI locational data can meet
the Agency's data standards for locational information, which require
metadata for the method, accuracy and description of what the latitude
and longitude coordinates represent.
Over the coming months, the Agency is implementing a program to
ensure that virtually all TRI facilities will have locational
information that meet the Agency's data standard requirements. An
implementation plan describing this program has been included in the
docket that accompanies this rule. Furthermore, through the IECP, EPA
provides the opportunity to correct inaccurate data maintained for use
by TRI data users.
1. Removal of Latitude/Longitude Reporting Requirement (Section 4.6
of Forms R and A). Three commenters recommended that reporters be
provided the opportunity to review and correct the latitude/longitude
data stored in EPA's FRS before removing section 4.6 from the reporting
forms and replacing it with locational data from FRS. One of the
commenters also recommended that EPA keep FRS locational data updated
in a timely manner.
While EPA does not agree with the commenters' suggestion on waiting
for facilities to review their locational data before removing part I
section 4.6 from the TRI reporting forms, EPA wholeheartedly agrees
with the commenters that TRI reporters should be allowed to review and
correct their latitude/longitude data in FRS. We are taking a number of
steps to provide this opportunity. Specifically, in the fall of 2005,
at the time of the electronic facility data release (eFDR), we will be
providing the relevant FRS locational information along with the
responses provided by the facility for the 2004 reporting year. This
will enable all interested parties, including data reporters and users
to compare the information contained in the most recent TRI submission
with the corresponding information for that facility in FRS.
Any interested party will have the opportunity to raise concerns
with TRI-reported latitude/longitude values or the new values to be
derived from FRS. These concerns may be submitted to the Agency through
the IECP (discussed above). The Agency plans to improve access to the
IECP to make it very easy for TRI reporters or data users to review and
notify the Agency of inaccurate locational values.
One commenter cautioned EPA that the definition of ``facility''
under EPCRA is not necessarily the same as the definition of
``facility'' under other statutes, and that this could affect the use
of FRS data. The commenter asserted that under EPCRA two sites that are
adjacent and/or contiguous and that are owned by the same entity are
considered to be one facility (even if separated by a public road).
However, according to the commenter, under RCRA the sites would be
considered two facilities. As such, there may be instances where the
data from each source is different for the same ``facility.''
Variation in facility definitions as one crosses EPA program
boundaries is one of the major challenges the Agency faces in its
efforts to develop a central facility registry. However, it is a
challenge which already faces some users of TRI information. For
example, users of information for RCRA assessments are already faced
with the challenge to create a map between multiple RCRA facilities and
a single TRI facility, when the facility definitions are not
consistent. Likewise, there may be cases where the TRI-reported RCRA
IDs do not constitute the totality of RCRA IDs associated with a given
TRIFID due to a limited number of spaces on the TRI form. Presently,
crosswalk checks are completed manually.
The conversion to the use of FRS for facility identification
information should actually strengthen the mapping across programs with
different facility definitions. To understand why this is so, one needs
to understand the meaning of a facility in FRS. In FRS, each entity
with a discrete street address is an independent facility. Where
individual programs will disagree is in the case of more complex
facilities where ownership or programmatic considerations have led to
the clustering of multiple FRS ``facilities'' into a single entity for
the purposes of a program (e.g., TRI).
A key step in the transition to the use of FRS supplied locational
data will be the creation of a program map. This map will use the 2004
TRI responses to assign a TRI facility identification number (TRIFID)
to each relevant FRS facility. Where multiple FRS facilities have the
same TRIFID, all will be assigned the same TRIFID. This map will ensure
that the locational information for the TRI facility contains not only
all relevant locational
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information, but also all relevant EPA program identification numbers.
Furthermore, the locational information retrieved will be superior to
current TRI information because it will have metadata describing how
the information was derived, its collection method, its probable
accuracy, and a geographic description (i.e., whether it is based on
the center of the production facility, a pipe outfall, stack, etc).
This change will provide a much more comprehensive look at all of the
locational information for TRI facilities. Furthermore, the enhanced
access to the IECP for data suppliers and users should result in a
steady improvement in facility mapping and locational information.
One commenter was troubled about how long it would take to populate
FRS with TRI data and complete data quality checks. The commenter urged
EPA to ensure that no lapses occur in the availability of locational
data as a result of this process.
EPA will ensure that there is no lapse in making locational data
available for TRI data users. Locational data from TRI and other
programs is already stored in FRS and the Agency will provide a
seamless transition from collecting locational data directly from TRI
reporters to pulling existing locational data out of FRS and providing
it along with other facility identification information to TRI data
users starting with the public data release for reporting year 2005
information, which must be submitted by July 1, 2006.
Several commenters expressed concern that EPA's FRS database does
not often have previously stored locational data for first-time TRI
reporters. The commenter asserted that this data gap problem could also
be exacerbated by the fact that not every state is participating in
EPA's Exchange Network. The commenter recommended that EPA modify the
rule to require reporting of locational data by first time reporters.
Another commenter stated that data gaps in the FRS database could be
best addressed by requiring new reporting entities to include
additional information on facility identification data the first time
they are required to complete Form R or A.
EPA acknowledges that there are a relatively small number of new
facilities that submit TRI Form R or A reports each year for which the
Agency does not already have locational data stored in FRS. The Agency
disagrees, however, that new reporters should be required to submit
locational data. EPA plans to use street address matching in
combination with its siting tool to populate FRS with locational data
for those cases in which FRS has no previous locational data for new
reporters. As discussed above, reporters, as well as the states and the
general public will be provided the opportunity to submit a request for
correcting inaccurate facility locational data by using the Agency's
IECP.
Two commenters opposed the use of address matching for deriving TRI
facility latitude/longitude data. One commenter stated that the two
most apparent problems with this method are: (1) If the facility is in
a rural or unpopulated area, offshore, etc., then the software may be
unable to match the address to a location; and (2) the facility's
mailing address may not be the location where the toxic chemical
releases occur. For example, if a facility picks up mail at a
headquarters building that manages several facilities, this would
create a different latitude/longitude than where its stacks are
located.
The second commenter claimed that as much as 70% of the locational
data derived from various EPA databases and stored in FRS may be based
on address matching. The commenter maintained that some of the
locational data in FRS may be based on wastewater outfall locations
that can be long distances from the facilities. Reliance on FRS data
collected from these other databases, according to the commenter, would
introduce significant error into the use of the information.
The Agency disagrees with these commenters. Dealing with the second
comment first, FRS does not use mailing addresses for locational
referencing of facilities. Rather, the actual street address of the
facility is used. EPA believes that street address matching, used in
combination with our facility siting tool (i.e., a geospacial
application that uses aerial imagery to determine latitude and
longitude coordinates) in rural areas, can provide credible locational
coordinates for all TRI facilities. EPA plans to use this method for
new reporters and for other cases in which no credible locational data
is available in FRS. The Agency believes that this method provides a
better source of data than locational data for which there is no
metadata (i.e., no explanation as to how the information was derived or
its accuracy), which occurs with the current locational data reported
to the TRI program. Furthermore, because the Agency plans to include
all locational information in the next e-FDR, anyone interested in a
particular facility will be able to easily raise concerns through the
IECP with the data chosen to represent the location of the facility.
As to the concern with the quality of FRS, FRS has been operational
since 2000 and continues to improve data quality. Many EPA programs
utilize FRS and the existing IECP process is in place to facilitate
receipt of suggested corrections to locational information. Despite
these facts, only a very small percentage of IECP requests have
involved locational updates. Further, for smaller facilities,
especially those most likely to rely on street addresses, we believe an
address is a reliable indicator of location.
Further, FRS will provide a complete picture of all locational
information available on a facility. Because FRS provides metadata for
the method, accuracy, and description of its locational data, it will
be possible to know exactly the nature of the point being measured. The
data user of such information will know whether they are using a point
based on an outfall, a stack, or the center of the production. To the
extent that a preferred location reported out of FRS is incongruent
with the intended use of the TRI information, the data user may simply
use another locational value for their purposes. This is a significant
improvement on the current TRI locational values of unknown accuracy
and relevance.
One commenter recommended that instead of removing section 4.6 from
the TRI reporting forms, facilities should instead certify that the
latitude and longitude data reported to TRI is obtained either from
EPA's Facility Siting Tool or from a Global Positioning System (GPS)
device. According to the commenter, this would ensure that facilities
provide more accurate information.
The Agency does not agree with the commenters that there is an
issue with the accuracy of locational information in FRS. Furthermore,
we do not agree that increasing reporting burden on TRI reporters to
provide locational data that is already available in FRS is an
appropriate response. Transitioning to FRS use for locational
information will allow users to not only have the most current
locational information, but a clear indication of the method of
collection, description of what is measured, and probable accuracy.
They will know the reference point of the facility (e.g., the street
address, a stack, or some permitted portion of the facility) for which
locational information is provided. Finally, use of FRS will improve
the overall quality of TRI facility locational information. FRS will be
continuously gathering the best locational information based on
metadata for the method, accuracy and description of what the latitude
and
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longitude coordinates represent--including GPS-based data--as opposed
to relying only on TRI-reported values of unknown precision.
Furthermore, as stated in response to several previous questions, the
IECP will provide yet another means for continually improving facility
identification information.
2. Removal of Reporting Requirements for EPA Permit and Program
Identification Numbers (Sections 4.8, 4.9 and 4.10 of Forms R and A).
Three commenters emphasized the importance of EPA facility
identification numbers to TRI data users, including various EPA program
offices and the general public. One commenter cited, as an example, the
use of Resource Conservation and Recovery Act (RCRA) identification
numbers to calculate ``double counting'' of TRI chemical disposal
transfers sent to TRI facilities that report the same chemicals again.
The commenter stated that RCRA Identification numbers (RCRA IDs) allow
transfers of chemicals (marked with RCRA IDs in section 6 of Form R) to
be matched up with receiving TRI facilities (marked with RCRA IDs in
section 4.8). The commenter also cited a 1998 report by a public
interest organization to demonstrate the usefulness of collecting EPA
program identification numbers in TRI. The report used the Underground
Injection Control identification numbers to help analyze the
completeness and accuracy of underground injection well data in EPA
databases. According to the commenter, these examples are just a small
sample of the many uses for this data. The commenter recommended that
EPA conduct a small study to demonstrate that FRS data is of equal or
higher quality to TRI's program identification data before removing
these data elements from the TRI reporting forms.
EPA agrees with the commenters that the EPA program identification
numbers in sections 4.8 through 4.10 of the TRI reporting forms are
important and are used extensively by various EPA offices, the states,
and the general public. This information will not be lost. Program
identification numbers previously reported through TRI are already
stored in the TRI database known as the Toxics Release Inventory System
(TRIS) and will be available to data users through access tools offered
by the Agency.
Nevertheless, in consideration of commenters' concerns, EPA
conducted a study of RCRA IDs and concluded that FRS provided higher
data quality than TRI reporting. In particular, the Agency examined
over 10,000 TRI forms with RCRA IDs from the 2002 Reporting Year. These
facilities were selected because they were used by the Office of Solid
Waste in its annual evaluation of waste minimization progress for
approximately thirty chemicals related to a Federal Government
Performance and Result Act (GPRA) goal. In its evaluation, the Office
of Solid Waste uses the RCRA IDs in conjunction with Form R sections 5
and 6 data to estimate the quantities of priority chemicals that may be
contained in hazardous versus non-hazardous wastes. This activity is
analogous to those of interest to the commenters.
Approximately 800 RCRA IDs were found in the TRI database that did
not match RCRA IDs in the RCRAInfo database. Almost half of these RCRA
IDs contained obvious transcription errors (i.e., ``o'' substituted for
``zero'', etc). It is not clear to what extent the remainder represent
more subtle transcription errors or other factors, although it is
important to note that the Office of Solid Waste maintains an active
data stewardship program. On the other hand, it is also important to
note that the TRI Reporting Form has only two spaces for the listing of
RCRA IDs. Because of differences in facility definitions, it is quite
reasonable to assume that a current TRI facility could be associated
with more than two RCRA IDs. Given these factors, and the fact that FRS
contains RCRA IDs assigned by EPA's RCRA program, there can be little
doubt that FRS is a more definitive source of information on RCRA IDs,
and that cross program coverage will be improved by conversion to the
use of FRS.
We believe that the few cases in which there may be information
gaps can be addressed by improving communication between EPA's Office
of Environmental Information, which operates both the TRI and FRS
programs, and the other Agency offices responsible for the program
identification data at issue. The one possible exception to this
statement relates to IDs for underground injection sites reported under
the UIC program. Presently, UIC IDs are not collected on the Federal
level except as a part of TRI. States maintain these records.
Unfortunately, because of form limitations, TRI reporters have not
necessarily provided a full listing of UIC permitted wells. EPA's
Office of Information Collection is working with the Office of Ground
Water and Drinking Water, however, to gather UIC information from
individual states to include in FRS. It is anticipated that states will
begin to provide this more complete information in 2006, in advance of
the first data release to be affected by this rule.
One commenter expressed concern about a time lag in the
availability of EPA program identification data if EPA removes the
program identification numbers from the TRI reporting forms. The
commenter cited the importance of this data to a variety of community
groups across the country and urged EPA to quickly address this
potential problem so the public would not experience a lag in its use
of TRI Explorer.
As discussed above, the FRS already stores EPA program
identification data. EPA will ensure that there is no lag in the
availability of such data in TRI Explorer or Envirofacts, the two EPA
data applications that TRI data users rely upon to access TRI-related
data. By the time that the 2006 TRI Public Data Release (PDR) is
published, all applicable FRS data will have been copied into the TRI
database for publication.
One commenter asserted that the EPA program identification numbers
on the TRI reporting forms are used by state environmental agencies as
a cross reference for other program applications. According to the
commenter, at least one state uses the data as a link to hazardous
waste generator reporting, in addition to its use as a key identifier
for TRI facilities. The commenter expressed concern that the proposed
rule did not address how states would receive these data elements if
they are not supplied with the Form R. The commenter contended that
many states have developed their own data systems to manage the TRI
reports filed with the state and they regard TRI reporting as a joint
EPA-State partnership since facilities are required to file their forms
at both the Federal and State levels. The commenter expressed concern
that the data elements states need to manage their TRI data will be
lost if this change is finalized.
EPA is committed to ensuring that states and TRI data users have
accurate program identification numbers associated with TRIFIDs.