Procedures for Prioritization of Chemicals for Risk Evaluation Under the Toxic Substances Control Act, 4825-4837 [2017-00051]
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[FR Doc. 2017–00743 Filed 1–13–17; 8:45 am]
BILLING CODE 6560–50–P
ACTION:
Proposed rule.
SUPPLEMENTARY INFORMATION:
As required under section
6(b)(1) of the Toxic Substances Control
Act (TSCA), EPA is proposing to
establish a risk-based screening process
and criteria that EPA will use to identify
chemical substances as either HighPriority Substances for risk evaluation,
or Low-Priority Substances for which
risk evaluations are not warranted at the
time. The proposed rule describes the
processes for identifying potential
candidates for prioritization, selecting a
candidate, screening that candidate
against certain criteria, formally
initiating the prioritization process,
providing opportunities for public
comment, and proposing and finalizing
designations of priority. Prioritization is
the initial step in a new process of
existing chemical substance review and
risk management activity established
under recent amendments to TSCA.
DATES: Comments must be received on
or before March 20, 2017.
ADDRESSES: Submit your comments,
identified by docket identification (ID)
number EPA–HQ–OPPT–2016–0636, by
one of the following methods:
• Federal eRulemaking Portal: https://
www.regulations.gov. Follow the online
instructions for submitting comments.
Do not submit electronically any
information you consider to be
Confidential Business Information (CBI)
or other information whose disclosure is
restricted by statute.
• Mail: Document Control Office
(7407M), Office of Pollution Prevention
and Toxics (OPPT), Environmental
Protection Agency, 1200 Pennsylvania
Ave. NW., Washington, DC 20460–0001.
• Hand Delivery: To make special
arrangements for hand delivery or
delivery of boxed information, please
follow the instructions at https://
www.epa.gov/dockets/contacts.html.
Additional instructions on commenting
or visiting the docket, along with more
information about dockets generally, is
available at https://www.epa.gov/
dockets.
SUMMARY:
FOR FURTHER INFORMATION CONTACT:
ENVIRONMENTAL PROTECTION
AGENCY
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40 CFR Part 702
[EPA–HQ–OPPT–2016–0636; FRL–9957–74]
RIN 2070–AK23
Procedures for Prioritization of
Chemicals for Risk Evaluation Under
the Toxic Substances Control Act
Environmental Protection
Agency (EPA).
AGENCY:
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For technical information contact:
Ryan Schmit, Immediate Office, Office
of Chemical Safety and Pollution
Prevention, Environmental Protection
Agency, 1200 Pennsylvania Ave. NW.,
Washington, DC 20460–0001; telephone
number: (202) 564–0610; email address:
schmit.ryan@epa.gov.
For general information contact: The
TSCA-Hotline, ABVI-Goodwill, 422
South Clinton Ave., Rochester, NY
14620; telephone number: (202) 554–
1404; email address: TSCA-Hotline@
epa.gov.
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I. Executive Summary
A. Does this action apply to me?
This proposed rule does not propose
to establish any requirements on
persons or entities outside of the
Agency. This action may, however, be of
interest to entities that are or may
manufacture or import a chemical
substance regulated under TSCA (e.g.,
entities identified under North
American Industrial Classification
System (NAICS) codes 325 and 324110).
Since other entities may also be
interested, the Agency has not
attempted to describe all the specific
entities and corresponding NAICS codes
for entities that may be interested in or
affected by this action.
B. What action is the agency taking?
EPA is proposing to establish the
internal processes and criteria by which
EPA will identify chemical substances
as either High-Priority Substances for
risk evaluation, or Low-Priority
Substances for which risk evaluations
are not warranted at the time.
C. Why is the agency taking this action?
This rulemaking is required by TSCA
section 6(b)(1)(A). Prioritization of
chemical substances for further
evaluation will ensure that the Agency’s
limited resources are conserved for
those chemical substances most likely to
present risks, thereby furthering EPA’s
overall mission to protect health and the
environment.
D. What is the agency’s authority for
taking this action?
EPA is proposing this rule pursuant to
the authority in TSCA section 6(b), 15
U.S.C. 2605(b). See also the discussion
in Units II.A and B.
E. What are the estimated incremental
impacts of this action?
This is a proposed rule that would
establish the processes by which EPA
intends to designate chemical
substances as either High or LowPriority Substances for risk evaluation.
It would not establish any requirements
on persons or entities outside of the
Agency. EPA did not, therefore, estimate
potential incremental impacts from this
action.
F. What should I consider as I prepare
my comments for EPA?
1. Submitting CBI. Do not submit this
information to EPA through
regulations.gov or email. Clearly mark
the part or all of the information that
you claim to be CBI. For CBI
information in a disk or CD–ROM that
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you mail to EPA, mark the outside of the
disk or CD–ROM as CBI and then
identify electronically within the disk or
CD–ROM the specific information that
is claimed as CBI. In addition to one
complete version of the comment that
includes information claimed as CBI, a
copy of the comment that does not
contain the information claimed as CBI
must be submitted for inclusion in the
public docket. Information so marked
will not be disclosed except in
accordance with procedures set forth in
40 CFR part 2.
2. Tips for preparing your comments.
When preparing and submitting your
comments, see the commenting tips at
https://www.epa.gov/dockets/
comments.html.
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II. Background
A. Recent Amendments to TSCA
On June 22, 2016, the President
signed into law the ‘‘Frank R.
Lautenberg Chemical Safety for the 21st
Century Act’’ (Pub. L. 114–182), which
imposed sweeping reforms to TSCA.
The bill received broad bipartisan
support in the U.S. House of
Representatives and Senate, and its
passage was heralded as the most
significant update to an environmental
law in over 20 years. The amendments
give EPA improved authority to take
actions to protect people and the
environment from the effects of
dangerous chemical substances.
Additional information on the new law
is available on EPA’s Web site at https://
www.epa.gov/assessing-and-managingchemicals-under-tsca/frank-rlautenberg-chemical-safety-21stcentury-act.
When TSCA was originally enacted in
1976, it established an EPAadministered health and safety review
process for new chemical substances
prior to allowing their entry into the
marketplace. However, tens of
thousands of chemical substances in
existence at that time were
‘‘grandfathered in’’ with no requirement
for EPA to ever evaluate their risks to
health or the environment. The absence
of a review requirement or deadlines for
action, coupled with a burdensome
statutory standard for taking risk
management action on existing
chemical substances, resulted in very
few chemical substances ever being
assessed for safety by EPA, and even
fewer subject to restrictions to address
identified risks.
One of the key features of the new law
is the requirement that EPA now
systematically prioritize and assess
existing chemical substances, and
manage identified risks. Through a
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combination of new authorities, a riskbased safety standard, mandatory
deadlines for action, and minimum
throughput requirements, TSCA
effectively creates a ‘‘pipeline’’ by
which EPA will conduct existing
chemical substances review and
management. This new pipeline—from
prioritization to risk evaluation to risk
management (when warranted)—is
intended to drive steady forward
progress on the backlog of existing
chemical substances left largely
unaddressed by the original law.
Prioritization is the initial step in this
process.
B. Statutory Requirements for
Prioritization
TSCA section 6(b)(1) requires EPA to
establish, by rule, the process and
criteria for prioritizing chemical
substances for risk evaluation.
Specifically, the law requires EPA to
establish ‘‘a risk-based screening
process, including criteria for
designating chemical substances as
high-priority substances for risk
evaluations or low-priority substances
for which risk evaluations are not
warranted at the time.’’ TSCA sections
6(b)(1) through (3) provide further
specificity on both the process and
criteria, including preferences for
certain chemical substances that EPA
must apply, the procedural steps,
definitions of High-Priority Substances
and Low-Priority Substances, and
screening criteria that EPA must
consider in designating a chemical
substance as either High-Priority
Substances or Low-Priority Substances.
The statutory requirements related to
prioritization are described in further
detail in this unit.
1. Prioritization Steps. Based on
TSCA sections 6(b)(1) through (3), EPA
is proposing to include four steps or
phases in prioritization: (1) PrePrioritization, (2) Initiation, (3)
Proposed Designation, and (4) Final
Designation. During the PrePrioritization phase, EPA is proposing
to apply the statutory preferences in
TSCA section 6(b)(2), along with other
criteria, to narrow the pool of potential
candidates, and identify a single
chemical substance (or category of
chemical substances) to screen against
the statutory criteria in TSCA section
6(b)(1)(A). Aside from the statutory
preferences listed, the law does not
direct or limit EPA in how it is to
ultimately select a chemical substance
on which to initiate prioritization,
requiring only that the process be ‘‘riskbased.’’ At the Initiation step, EPA must
announce a candidate chemical
substance and give the public a 90-day
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comment period to submit relevant
information. 15 U.S.C. 2605(b)(1)(C)(i).
At the Proposed Designation step, EPA
must propose to designate a chemical
substance as either a High-Priority
Substance or a Low-Priority Substance,
publish the proposed designation and
the information, analysis, and basis
used to make the designation, and take
public comment a second time for 90
days. 15 U.S.C. 2605(b)(1)(C)(ii). At
Final Designation, EPA must either
finalize a High-Priority Substance
designation and initiate a risk
evaluation, or finalize a Low-Priority
Substance designation in which case it
will not conduct a risk evaluation on the
chemical substance unless and until
information leads EPA to revisit that
priority designation. 15 U.S.C.
2605(b)(3)(A) and (B).
2. Screening criteria and statutory
preferences. The statute defines a HighPriority Substance as one that the
Administrator concludes, without
consideration of costs or other non-risk
factors, may present an unreasonable
risk of injury to health or the
environment because of a potential
hazard and a potential route of exposure
under the conditions of use, including
an unreasonable risk to potentially
exposed or susceptible subpopulations
identified as relevant by the
Administrator. 15 U.S.C.
2605(b)(1)(B)(i). Conversely, the law
specifies that a Low-Priority Substance
is one that the Administrator concludes,
based on information sufficient to
establish, without consideration of costs
or other non-risk factors, does not meet
the standard for designating a chemical
substance a High-Priority Substance. 15
U.S.C. 2605(b)(1)(B)(ii).
In designating the priority of a
chemical substance, EPA must screen a
candidate chemical substance against
certain criteria specified in TSCA
section 6(b)(1)(A). These include the
hazard and exposure potential of the
chemical substance (e.g., persistence
and bioaccumulation, potentially
exposed or susceptible subpopulations,
and storage near significant sources of
drinking water), the conditions of use or
significant changes in the conditions of
use of the chemical substance, and the
volume or significant changes in the
volume of the chemical substance
manufactured or processed. EPA
interprets ‘‘significant changes in’’
conditions of use to have relevance
primarily in the context of revising a
priority designation. With respect to an
initial prioritization decision, any
changes in use that have occurred in the
past would already be captured by the
concept of ‘‘conditions of use,’’ as
defined in TSCA section 3.
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The results of this screen will help
inform EPA’s proposed priority
designation. However, given that the
statutory deadlines are triggered at the
initiation of prioritization, and that EPA
will want to have a good understanding
of the chemical substance before
triggering those deadlines, EPA will
consider these screening criteria earlier
in the process. As discussed in more
detail in Unit III., EPA is therefore
proposing to include the screening
review in the rule as part of the preprioritization phase.
In designating High-Priority
Substances, EPA is to give preference to
chemical substances that are listed in
the 2014 Update of the TSCA Work Plan
for Chemical Assessments (Ref. 1) that:
(1) Have persistence and
bioaccumulation scores of 3; and (2) are
known human carcinogens and have
high acute and chronic toxicity. 15
U.S.C. 2605(b)(2)(D). The law further
requires that 50% of all ongoing risk
evaluations be drawn from the 2014
Update to the TSCA Work Plan for
Chemical Assessments, meaning that, at
least at the outset of the program, EPA
will need to draw at least 50% of HighPriority Substance designations from the
same list. 15 U.S.C. 2605(b)(2)(B).
3. Metals and metal compounds.
When prioritizing metals or metal
compounds, EPA must use the March
2007 Framework for Metals Risk
Assessment of the Office of the Science
Advisor (Ref. 2) (or a successor
document that addresses appropriate
considerations for conducting a risk
assessment on a metal or metal
compound and is peer reviewed by the
Science Advisory Board). 15 U.S.C.
2605(b)(2)(E). However, during the
prioritization process, EPA will not be
conducting chemical risk assessments;
and, consequently, much of this
guidance will not be directly relevant.
EPA interprets this provision to ensure
that the analysis and considerations
during the prioritization process take
into account the special attributes and
behaviors of metals and metal
compounds that are relevant to
judgments of risk. For example, this
might include consideration of the
document’s Key Principles that
differentiate inorganic metals and metal
compounds from organic and
organometallic compounds, and their
unique attributes, properties, issues, and
processes. Because EPA will not
conduct risk assessments on metals or
metal compounds for purposes of
prioritization, EPA will not refer to
sections that provide guidance on how
to incorporate the Key Principles into
risk assessments.
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4. Timeframe. TSCA requires that the
prioritization process last between nine
and twelve months. 15 U.S.C.
2605(b)(1)(C). This timeframe takes on
particular significance, given that the
statute does not authorize EPA to
‘‘pause’’ or delay the prioritization once
it has been initiated, and that a final
High-Priority Substance designation
results in the chemical substance
moving immediately into a risk
evaluation process that must be
generally completed within three years.
15 U.S.C. 2605(b)(4)(G).
5. Opportunities for public
participation. As already mentioned,
TSCA requires EPA to provide two 90day public comment periods during
prioritization—one following initiation,
and a second following a proposed
designation. 15 U.S.C. 2605(b)(1)(C)(i)
and (ii). TSCA further requires that EPA
include a process for extending the
comment deadline for up to three
months in order to receive or evaluate
information coming from a TSCA
section 4 test order. 15 U.S.C.
2605(b)(1)(C)(iii). These public
comment periods, coupled with the
nine month minimum timeframe for
prioritization, ensure that the public
will be on notice of EPA’s intention to
further evaluate a chemical’s risks and
will have opportunity to engage early in
the process before the risk evaluation
has started.
6. Default to High-Priority Substance
Designation. If, after prioritization has
been initiated, the public has been given
an opportunity to submit relevant
information, and EPA has extended the
comment period pursuant to TSCA
section 6(b)(1)(C)(iii) in order to receive
or evaluate additional information, EPA
determines that the available
information is insufficient to enable the
designation of the chemical substance as
a Low-Priority Substance, the statute
requires EPA to propose a High-Priority
Substance designation. 15 U.S.C.
2605(b)(1)(C)(iii). Based in part on this
provision, and as discussed further in
Unit III, EPA is proposing to require a
default-to-high in all cases in which
insufficient information exists to
designate the chemical as a Low-Priority
Substance at both the proposed and
final designation.
7. Initial ten chemicals for risk
evaluation. TSCA requires EPA to,
within six months of enactment, ensure
that risk evaluations are being
conducted on ten chemical substances
drawn from the 2014 update of the
TSCA Work Plan for Chemical
Assessments, and to publish a list of
those chemical substances during that
same period. 15 U.S.C. 2605(b)(2)(A).
The initial ten chemical substances are
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not subject to the prioritization process
or the procedures in this rule. However,
completion of these risk evaluations
triggers the ongoing designation
requirement discussed in Unit II.B.8.
8. Ongoing designations. Upon
completion of a risk evaluation (other
than those requested by a manufacturer
pursuant to TSCA section 6(b)(4)(C)(ii)),
EPA must designate at least one
additional High-Priority Substance to
take its place. 15 U.S.C. 2605(b)(2)(C).
Because designation as a High-Priority
Substance results in the chemical
substance moving immediately to risk
evaluation, this provision prevents the
number of existing chemical substances
undergoing risk evaluation from ever
decreasing over time. In addition, EPA
must designate at least twenty chemical
substances as High-Priority Substances
by three and one half years after
enactment, effectively doubling the
number of chemical substances in the
review pipeline. 15 U.S.C. 2605(b)(2)(B).
The statute also requires that at least
twenty chemical substances be
designated as Low-Priority Substances
by three and one half years after
enactment, but without a comparable
requirement to continue designating
additional Low-Priority Substances after
that. 15 U.S.C. 2605(b)(2)(B), (b)(3)(C).
Although EPA must continue to
prioritize and evaluate chemical
substances ‘‘at a pace consistent with
the ability of the Administrator to
complete risk evaluations in accordance
with the deadlines,’’ this provision does
not modify the minimum throughput or
other ongoing designation requirements
for High-Priority Substances. 15 U.S.C.
2605(b)(2)(C). It does, however, suggest
that EPA must have adequate resources
should EPA plan to designate more than
twenty chemical substances as HighPriority Substances at any given time.
9. Revision of designation. TSCA
allows the Administrator to revise the
designation of a Low-Priority Substance
to a High-Priority Substance ‘‘based on
information made available to the
Administrator.’’ 15 U.S.C. 2605(b)(3)(B).
This provision does not restrict the basis
for a revision to the discovery or receipt
of new information. For example, EPA
could also justify a revision based on
information that was available but was
not considered at the time of the
original prioritization decision, or
information that was considered but
which EPA now views differently as a
result of changes in scientific
understanding (e.g., changes in
scientific understanding of how a
chemical can enter or interact with the
human body).
10. Other relevant statutory
requirements. TSCA imposes new
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requirements on EPA in a number of
different areas that EPA is not proposing
to incorporate or otherwise address in
this proposed rule. For example,
amendments to TSCA section 4 require
EPA to ‘‘. . . reduce and replace, to the
extent practicable, [. . .] the use of
vertebrate animals in the testing of
chemical substances . . .’’ and to
develop a strategic plan to promote such
alternative test methods. 15 U.S.C.
2603(h). Likewise, TSCA section 26
requires, to the extent that EPA makes
a decision based on science under TSCA
sections 4, 5, or 6, that EPA use certain
scientific standards and base those
decisions on the weight of the scientific
evidence. 15 U.S.C. 2625(h) and (i).
While these requirements are relevant to
the prioritization of chemical
substances, EPA is not obliged to
include them in this proposed rule. By
their express terms, these statutory
requirements apply to EPA’s decisions
under TSCA section 6, without the need
for regulatory action. Moreover, in
contrast to TSCA section 6, Congress
has not directed EPA to implement
these other requirements ‘‘by rule;’’ it is
well-established that where Congress
has declined to require rulemaking, the
implementing agency has complete
discretion to determine the appropriate
method by which to implement those
provisions. E.g., United States v. Storer
Broadcasting Co., 351 U.S. 192 (1956).
A number of stakeholders raised
questions as to whether EPA should
define a number of important terms in
this rule (e.g., ‘‘best available science’’,
‘‘weight-of-the-evidence’’, ‘‘sufficiency
of information’’, ‘‘unreasonable risk’’,
and ‘‘reasonably available
information’’). Many of the terms used
in the proposed rule are not novel
concepts and are already in use, and
their meaning is discussed extensively
in existing Agency guidance. For
example, extensive descriptions for the
phrases ‘‘best available science’’,
‘‘weight-of-the-evidence’’, and
‘‘sufficiency of information’’ can be
found in EPA’s Risk Characterization
Handbook (Ref. 3), and in other existing
Agency guidance.
EPA believes further defining these
and other terms in the proposed rule is
unnecessary and ultimately
problematic. These terms have and will
continue to evolve with changing
scientific methods and innovation.
Codifying specific definitions for these
phrases in this rule may inhibit the
flexibility and responsiveness of the
Agency to quickly adapt to and
implement changing science. The
Agency intends to use existing guidance
definitions and to update definitions
and guidance as necessary.
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While EPA is seeking public comment
on all aspects of this proposed rule, the
Agency is specifically requesting public
input on this issue. The Agency
welcomes public comments regarding
the pros and cons of codifying these or
other definitions and/or approaches for
these or any other terms. EPA
encourages commenters to suggest
alternative definitions the Agency
should consider for codification in this
procedural rule. Please explain your
views as clearly as possible, providing
specific examples to illustrate your
concerns and suggest alternate wording,
where applicable.
C. Prioritization Under the 2012 TSCA
Work Plan Methodology
Prioritization of chemical substances
for review is not a novel concept for the
Agency. In 2012, EPA released the
TSCA Work Plan Chemicals: Methods
Document in which EPA described the
process the Agency intended to use to
identify potential candidate chemical
substances for near-term review and
assessment under TSCA (Ref. 4). EPA
also published an initial list of TSCA
Work Plan chemicals identified for
further assessment under TSCA as part
of its chemical safety program in 2012
(Ref. 5), and an updated list of chemical
substances for further assessment in
2014 (Ref. 1). The process for
identifying these chemical substances
was based on a combination of hazard,
exposure, and persistence and
bioaccumulation characteristics.
Congress expressly recognized the
validity of EPA’s existing prioritization
methodology for the TSCA Work Plan.
For example, the law requires that EPA
give certain preferences to chemical
substances listed on the 2014 Update to
the TSCA Work Plan. 15 U.S.C.
2605(b)(2)(D). Moreover, the law
requires that at least 50 percent of all
ongoing risk evaluations be drawn from
the 2014 Update to the TSCA Work
Plan. 15 U.S.C. 2605(b)(2)(B). The
statutory screening criteria in TSCA
section 6(b)(1)(A) also significantly
overlaps with the considerations in the
Work Plan methodology (e.g.,
persistence, bioaccumulation, toxicity,
carcinogenicity, etc.).
However, there are a number of key
differences between EPA’s TSCA Work
Plan process and the prioritization
process that TSCA now requires. First,
the Work Plan process involved culling
through thousands of chemical
substances to create a list that EPA
could, over time and without prescribed
deadlines, focus its limited resources
on. The TSCA Work Plan did not
require EPA to assess listed chemical
substances, and included no deadlines
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for completing risk assessments or
addressing identified risks.
Prioritization under this proposed rule
will involve a similar culling, but upon
designating a chemical substance as a
High-Priority Substance, the Agency
must start a risk evaluation, and
generally complete that evaluation
within a specified amount of time. If
EPA determines in the risk evaluation
that a chemical substance presents an
unreasonable risk of injury to health or
the environment, EPA must also initiate
a risk management rulemaking subject
to statutory deadlines. 15 U.S.C.
2605(c). As such, EPA will need to be
judicious in selecting the chemical
substances that go into prioritization.
Further, while chemical substances
listed on the TSCA Work Plan were
likely to be well-characterized for
hazard and have at least some
information indicating potential
exposure, Work Plan chemical
substance assessments have generally
focused on specific chemical uses.
Given the statutory deadlines, EPA
generally intends to ensure it has a more
complete set of data upfront that would
allow EPA to evaluate a chemical
substance under all conditions of use (a
broader scope) within the statutory
deadlines. For chemical substances with
insufficient information to conduct a
risk evaluation, EPA generally expects
to pursue a significant amount of data
gathering before initiating prioritization.
Finally, the TSCA Work Plan process
focused solely on identifying potential
high risk chemical substances for
further review. Because the statute also
requires the identification of LowPriority Substances—those chemical
substances that EPA has determined,
based on sufficient evidence, do not
warrant further review at the time—EPA
will need to undertake new and
different analyses than it has done to
date under the TSCA Work Plan.
While EPA has drawn from the TSCA
Work Plan methodology and EPA’s
experience in implementing that
process in developing this proposed
rule, EPA is proposing to tailor the
process for prioritization to the specific
requirements in the new statute.
D. Stakeholder Involvement
On August 10, 2016, EPA held a one
day public meeting to hear from
stakeholders to better understand their
viewpoints on the development of the
prioritization rule. The meeting began
with a presentation from EPA on how
the Agency has prioritized chemicals for
further review under the TSCA Work
Plan methodology. The remainder of the
day was reserved for public comment.
Commenters had approximately four
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minutes to present their comments
orally and there was a total of 28 oral
comments on the prioritization rule.
Further information is available on
EPA’s Web site at https://www.epa.gov/
assessing-and-managing-chemicalsunder-tsca/meetings-and-webinarsamended-toxic-substances-control.
Stakeholders were also able to
provide written comments. EPA
received 50 written comments on the
prioritization rule, although many of
those who presented orally also
submitted written versions as well.
These comments and a transcript of the
meeting are accessible in the meeting’s
docket, identified by Docket ID No.
EPA–HQ–OPPT–2016–0399, available
online at https://www.regulations.gov/.
The commenters included
representatives from industry,
environmental groups, academics,
private citizens, trade associations, and
health care representatives, and
provided a diversity of perspectives.
Overall, there was a general expression
of support for the new law and EPA’s
inclusive approach to implementation
to date. Most groups agreed that the
prioritization rule had the potential to
increase transparency in EPA’s chemical
substance review and management
process, and urged the Agency to work
towards this goal.
A number of commenters suggested
codifying specific details in the rule,
such as a system for scoring and ranking
chemical substances; a listing of the
specific hazard and exposure
information upon which EPA will base
prioritization decisions; and definitions
of terms referenced in the statute like
‘‘weight of evidence’’ and ‘‘best
available science.’’ Others encouraged
EPA to keep the rules focused on a
framework for general process, to retain
Agency discretion where appropriate,
and to reserve specific scientific
considerations for Agency guidance.
EPA considered all of these comments
in the development of this proposed
rule, and welcomes additional feedback
from stakeholders on the Agency’s
proposed process for chemical
substance prioritization as presented in
this document.
III. Summary of Proposed Rule
This proposed rule incorporates all of
the elements required by statute, but
also supplements those requirements
with additional criteria the Agency
expects to consider, some clarifications
for greater transparency, and additional
procedural steps to ensure effective
implementation. Specific components of
the approach are discussed in this unit.
EPA requests comments on all aspects
of this proposed rulemaking.
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A. Policy Objective
The prioritization process under
TSCA is the principal gateway to risk
evaluation. EPA is ultimately making a
judgment as to whether or not a
particular chemical substance warrants
further assessment. As a general matter,
the overall objective of the process
should be to guide the Agency towards
identifying the High-Priority Substances
that have the greatest hazard and
exposure potential first. EPA may also
consider the relative hazard and
exposure of a potential candidate’s
likely substitute(s) in order to avoid
moving the market to a chemical
substance of equal or greater risks.
However, the prioritization process is
not intended to be an exact scoring or
ranking exercise and EPA is not
proposing such a system in this rule.
The precise order in which EPA
identifies High-Priority Substances (all
of which must meet the same statutory
standard) should not be allowed to slow
the Agency’s progress towards fully
evaluating the risks from those chemical
substances. Further, the level of analysis
necessary to support an exact ranking
system is not appropriate at the
prioritization stage, where the sole
outcome is a decision on whether EPA
will further evaluate the chemical
substance. EPA intends to conserve its
resources and the Agency’s deeper
analytic efforts for the actual risk
evaluation. This policy objective is
stated directly in the proposed rule.
Low-Priority Substance designations
serve some of the same policy
objectives. Although the statute does not
require EPA to designate more than
twenty Low-Priority Substances, doing
so ensures that chemical substances
with clearly low hazard and exposure
potential are taken out of consideration
for further assessment, thereby
conserving resources for the chemical
substances with the greatest potential
risks. There is also value in identifying
Low-Priority Substances as part of this
process, as it gives the public notice of
chemical substances for which potential
risks are likely low or nonexistent, and
industry some insight into which
chemical substances are likely not to be
regulated under TSCA.
B. Scope of Designations
EPA will designate the priority of a
‘‘chemical substance,’’ as a whole,
under this established process, and will
not limit its designation to a specific use
or subset of uses of a chemical
substance. EPA is proposing this in
response to clear statutory directives:
The relevant provisions of TSCA section
6 repeatedly refer to both the
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designation and evaluation of ‘‘chemical
substances’’ under the ‘‘conditions of
use.’’ ‘‘Conditions of use’’ are broadly
defined as ‘‘the circumstances, as
determined by the Administrator, under
which a chemical substance is intended,
known, or reasonably foreseen to be
manufactured, processed, distributed in
commerce, used, or disposed of.’’ 15
U.S.C. 2602.
Although some commenters at the
public meeting suggested that the
prioritization process should allow EPA
to designate a specific use of a chemical
substance as a High-Priority Substance
or a Low-Priority Substance, EPA does
not interpret the statute to support such
an interpretation. To the contrary, the
addition of the phrase ‘‘conditions of
use’’ (emphasis added) was intended to
move the Agency away from its past
practice of assessing only narrow uses of
a chemical substance, towards a
comprehensive approach to chemical
substance management. While EPA
clearly retains some discretion in
determining those conditions of use, as
a matter of law, EPA considers that it
would be an abuse of that discretion to
simply disregard known, intended, or
reasonably foreseen uses in its analyses.
C. Timeframe
As discussed in Unit II., TSCA section
6(b)(1)(C) requires that the prioritization
process last between nine and twelve
months. EPA is proposing in this rule
that initiation of the prioritization
begins upon publication of a notice in
the Federal Register that identifies a
chemical substance for prioritization
and provides the results of the screening
review. The process is complete upon
publication of a notice in the Federal
Register announcing a final priority
designation. Accordingly, the proposed
rule specifies that the process—from
initiation to final designation—shall last
between 9 and 12 months.
This timeframe serves dual purposes.
The minimum 9-month timeframe
ensures that the general public;
potentially-affected industries; state,
tribal and local governments;
environmental and health nongovernmental organizations; and others
have ample notice of upcoming federal
action on a given chemical substance,
and opportunity to engage with EPA
early in the process. The 12-month
maximum timeframe, coupled with the
default-to-high provision discussed
later, keeps the existing chemical
substances review pipeline in a forward
motion, and prevents EPA from getting
mired in analysis before ever reaching
the risk evaluation step.
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D. Categories of Chemical Substances
TSCA section 26 provides EPA with
authority to take action on categories of
chemical substances. 15 U.S.C. 2625(c).
‘‘Category of Chemical Substances’’ is
defined at 15 U.S.C. 2625(c)(2)(A).
Although the proposed rule most often
references ‘‘chemical substances,’’ EPA
is also proposing to include a clear
statement in the regulation that nothing
in the proposed rule shall be construed
as a limitation on EPA’s authority to
take action with respect to categories of
chemical substances, and that, where
appropriate, EPA can prioritize and
evaluate categories of chemical
substances.
E. Chemicals Subject to Prioritization
Generally, all chemical substances
listed on the TSCA Inventory are subject
to prioritization. TSCA contemplates
that, over time, all chemical substances
on the TSCA Inventory will be
prioritized into either High- or LowPriority Substances, and that all HighPriority Substances will be evaluated.
EPA notes that chemical substances
newly added to the TSCA Inventory
following EPA’s completion of premanufacture review under section 5 of
TSCA (15 U.S.C. 2604) are also
candidates for prioritization, although
EPA expects that such chemical
substances are not likely to be HighPriority candidates in light of the riskrelated determination that the Agency
must make pursuant to TSCA section
5(a)(3).
TSCA further requires EPA to go
through a separate process of
determining which chemical substances
on the TSCA Inventory are still actively
being manufactured, and EPA has
initiated a separate rulemaking for that
purpose (RIN 2070–AK24). This
distinction will inform EPA’s exposure
judgments during the prioritization
process. However, there is nothing in
TSCA that prohibits EPA from initiating
the prioritization process on an
‘‘inactive’’ chemical substance and
ultimately designating that chemical
substance as either a High-Priority
Substances (e.g., if exposures of concern
arise from ongoing uses) or Low-Priority
Substance.
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F. Pre-Prioritization Considerations
As discussed earlier, TSCA requires
that EPA establish a process, including
criteria for designating a chemical
substance as either a High-Priority
Substances or Low-Priority Substance.
15 U.S.C. 2605(b)(1). Aside from the
statutory preferences for chemical
substances on the 2014 Update to the
TSCA Work Plan (Ref. 1), the statute
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leaves EPA with broad discretion to
choose which chemical substance to put
into that process. Accordingly, this
proposed rule includes a discussion of
the criteria EPA expects to use to cull
through the chemical substances on the
TSCA Inventory. These include criteria
that will be used to identify potential
candidates for High-Priority Substances
or Low-Priority Substances, and that
describe how the extent of available
information on potential candidates will
affect whether they are selected for
prioritization.
For example, in identifying potential
candidates for High-Priority Substance
designations, EPA is proposing to seek
to identify chemical substances where
available information suggests that the
chemical substance may present a
hazard and that exposure is present
under ‘‘one or more conditions of use,’’
but where an ‘‘unreasonable risk’’
determination cannot be made without
a more extensive or complete
assessment in a risk evaluation. EPA
interprets the statutory definition of a
High-Priority Substance (‘‘. . . may
present an unreasonable risk [. . .]
because of a potential hazard and a
potential route of exposure . . .’’) to set
a fairly low bar, and EPA expects that
a large number of chemical substances
will meet this definition. Although EPA
will prioritize a ‘‘chemical substance’’
as a whole, EPA may base its
identification of a potential candidate as
a High-Priority Substance, and
ultimately the proposed designation, on
a single condition of use, provided the
hazard and exposure associated with
that single use support such a
designation. This proposal is based on
the statutory definition of a HighPriority Substance, which is clear that
the standard for the chemical as a whole
can be met based on a single condition
of use (‘‘. . . because of a potential
hazard and a potential route of exposure
. . .’’).
Conversely, in identifying potential
candidates for Low-Priority Substance
designation, EPA is proposing that it
will seek to identify chemical
substances where the information
indicates that hazard and exposure
potential for ‘‘all conditions of use’’ are
so low that EPA can confidently set that
chemical substance aside without doing
further evaluation. By comparison, then,
TSCA’s definition of Low-Priority
Substance (‘‘. . . based on sufficient
information, such substance does not
meet the standard for [. . .] a highpriority substance . . .’’) is fairly
rigorous, and effectively requires EPA to
determine that under no condition of
use does the chemical meet the HighPriority Substance standard.
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Consequently, EPA expects it will be
more difficult to support such
designations. Unlike High-Priority
Substances, EPA will not be able to
designate a chemical substance as a
Low-Priority Substance without first
looking at all of the conditions of use.
While not determinative, EPA believes
that its Safer Chemicals Ingredients List
(SCIL) (Ref. 6) will be a good starting
point for identifying potential
candidates for Low-Priority Substance
designations.
EPA is also proposing to include the
following list of additional exposure
and hazard considerations that can be
used to narrow the field of potential
candidates: (1) Persistent,
bioaccumulative, and toxic; (2) Used in
children’s products; (3) Used in
consumer products; (4) Detected in
human and/or ecological biomonitoring
programs; (5) Potentially of concern for
children’s health; (6) High acute and
chronic toxicity; (7) Probable or known
carcinogen; (8) Neurotoxicity; or (9)
Other emerging exposure and hazard
concerns to human health or the
environment, as determined by the
Agency. These criteria are drawn from
EPA’s 2012 TSCA Work Plan
methodology (Ref. 4), which, as
discussed earlier, was the process EPA
had been using to prioritize chemical
substances for assessment under TSCA.
EPA will evaluate one or more of these
nine considerations, and chemical
substances that meet one or more of
these criteria may be identified as
potential candidates for High-Priority
Substance designations. For example, if
a chemical substance is highly toxic and
used in consumer products, EPA may
wish to consider that chemical
substance as a potential High-Priority
Substance candidate. EPA may also
choose to identify potential candidates
based on other criteria that suggest the
chemical substance may otherwise
present a human health or
environmental concern, as
contemplated in the ‘‘catch-all’’
provision (9). The fact that a chemical
substance meets one of these criteria is
not determinative of an outcome,
including whether or not EPA will
select the chemical substance to go into
the prioritization process and/or the
priority designation that the chemical
substance will ultimately receive.
Conversely, chemical substances that
meet none of these criteria may be good
potential candidates for Low-Priority
Substance designation. The
considerations are intended to serve as
a general guide for the Agency, based on
EPA’s current understanding of
important considerations regarding
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potential chemical risk. It should also be
noted that while these considerations
are drawn from EPA’s 2012 Work Plan
methodology (Ref. 4), EPA will apply
them differently for prioritization. In the
TSCA Work Plan context, only chemical
substances that met these initial criteria
were eligible for listing on Work Plan.
For purposes of prioritization under
TSCA, the considerations do not
determine eligibility, but rather are
designed to help EPA to narrow its
focus.
G. Information Availability
Another key consideration in the preprioritization phase is the existence and
availability of risk-related information
on a candidate or potential candidate
chemical substance. Because EPA must
complete its prioritization process
within 12 months once prioritization
has been initiated for a chemical
substance, immediately initiate a risk
evaluation for High-Priority Substance,
and complete the risk evaluation within
three years of initiation, EPA cannot
assume that it will be able to require the
generation of critical information during
these time frames. Furthermore, the
statute does not grant EPA the
discretion to significantly delay either of
these processes, pending development
of information. Consequently, prior to
initiating the prioritization process for a
chemical substance, EPA will generally
review the available hazard and
exposure-related information, and
evaluate whether that information
would be sufficient to allow EPA to
complete both prioritization and risk
evaluation processes. As part of such an
evaluation, EPA expects to consider the
quality, objectivity, utility, and integrity
of the available information. To the
extent the information is not currently
available or is insufficient, EPA will
determine whether or not information
can be developed and collected,
reviewed and incorporated into analyses
and decisions in a timely manner. The
proposed rule makes it clear that
sufficiency of available information is
likely to be a crucial factor in the
selection of the chemical substances
that EPA chooses to put into the
prioritization process.
As noted, if information gaps are
identified during the prioritization or
risk evaluation processes, EPA expects
that it could be difficult to require the
development of necessary chemical
substance information, and receive,
evaluate, and incorporate that
information into analyses and decisions
within the statutory timeframes. Tests
necessary for risk evaluation, for
example, could take months or years to
develop and execute, plus additional
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time for EPA to issue the order or rule,
and to collect, review and incorporate
the new information. To avoid such a
scenario, EPA believes that it will need
to do a significant amount of upfront
data gathering and review. This
approach ensures that EPA stays on
track to meet relevant statutory
deadlines—particularly those for risk
evaluation.
The proposed rule makes clear that
EPA generally expects to use this new
authority, as appropriate and necessary,
to gather the requisite information prior
to initiating prioritization. This could
include, as appropriate, TSCA
information collection, testing, and
subpoena authorities, including those
under TSCA sections 4, 8, and 11(c), to
develop needed information.
Given the importance of ensuring that
sufficient information is available to
conduct the prioritization and risk
evaluation processes, EPA is proposing
to include this consideration during the
earliest stage in the process: During the
identification of potential candidates.
However, this criterion remains relevant
even after EPA has selected a candidate
and screened that chemical substance
against the statutory criteria in TSCA
section 6(b)(1)(A). Thus, if at any time
prior to the publication of a notice in
the Federal Register initiating
prioritization, EPA determines that
more information will be necessary to
support a prioritization designation or a
subsequent risk evaluation, EPA can
choose not to initiate prioritization for
that chemical substance pending
development of additional information.
H. Selection and Screening of a
Candidate Chemical Substance
As noted in Unit II., TSCA requires
that EPA give preference to chemical
substances listed in the 2014 update of
the TSCA Work Plan for Chemical
Assessments that (1) have a Persistence
and Bioaccumulation Score of 3; and (2)
are known human carcinogens and have
high acute and chronic toxicity. TSCA
section 6(b)(2)(B) further requires that
50 percent of all ongoing risk
evaluations be drawn from the 2014
Update to the TSCA Work Plan for
Chemical Assessments, meaning that
EPA will need to draw at least 50
percent of High-Priority Substance
candidates from the same list. By
operation of the statute, TSCA requires
that all TSCA Work Plan chemical
substances eventually be prioritized.
However, it is premature to presume
that those chemical substances will
necessarily be prioritized as HighPriority Substances, or that EPA would
find unreasonable risk.
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Aside from these statutory
preferences, however, TSCA does not
limit how EPA must ultimately select a
candidate chemical substance to put
into the prioritization process. EPA is
proposing that it will select a
candidate—for either High-Priority
Substances or Low-Priority Substance—
based on the policy objectives described
in Unit III.A. and the pre-prioritization
considerations described in Unit III. F.
and G. The development of the
proposed rule, including these policy
objectives, considerations and criteria,
was informed by EPA’s experience
implementing the 2012 TSCA Work
Plan methodology, which has been the
Agency’s primary tool for identifying
candidate chemical substances for
further assessment under TSCA. In
addition, EPA fully recognizes the
important role that stakeholders can
play in helping the Agency to identify
candidates for prioritization or to better
understand the unique uses or
characteristics of a particular chemical.
EPA continues to welcome this type of
engagement and dialogue early in the
process, including during the preprioritization phase. While the proposed
rule provides multiple opportunities for
public feedback during the
prioritization process, EPA is requesting
comment on whether and how EPA
should solicit additional input at the
pre-prioritization phase. Further, given
EPA’s objective to avoid simply moving
the market to substitute chemical
substances of equal or greater risks, EPA
requests comment on whether and how
information on the availability of
chemical substitutes should be taken
into account during this phase of the
prioritization process.
Once a single candidate chemical
substance (or category of chemical
substances) is selected, EPA will screen
the selected candidate against the
specific criteria and considerations in
TSCA section 6(b)(1)(A). Those criteria
and considerations are: (1) The chemical
substance’s hazard and exposure
potential; (2) the chemical substance’s
persistence and bioaccumulation; (3)
potentially exposed or susceptible
subpopulations; (4) storage of the
chemical substance near significant
sources of drinking water; (5) the
chemical substance’s conditions of use
or significant changes in conditions of
use; and (6) the chemical substance’s
production volume or significant
changes in production volume. Because
TSCA does not prohibit EPA from
expanding the statutory screening
criteria, the proposed rule also provides
an additional criterion: (7) Any other
risk-based criteria relevant to the
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designation of the chemical substance’s
priority, in EPA’s discretion. This final
criterion allows the screening review to
adapt with future changes in our
understanding of science and chemical
risks. In addition, EPA fully recognizes
the important role that stakeholders can
play in helping the Agency to identify
candidates for prioritization or to better
understand the unique uses or
characteristics of a particular chemical.
EPA continues to welcome this type of
engagement and dialogue early in the
process, including during the preprioritization phase. While the proposed
rule provides multiple opportunities for
public feedback during the
prioritization process, EPA is requesting
comment on whether and how EPA
should solicit additional input at the
pre-prioritization phase.
The screening review is not a risk
evaluation, but rather a review of
available information on the chemical
substance that relates to the screening
criteria. EPA expects to evaluate all
relevant sources of information while
conducting the screening review,
including, as appropriate, the hazard
and exposure sources listed in
Appendices A and B of the 2012 TSCA
Work Plan methodology (Ref. 4).
Ultimately, the screening review and
other considerations during the preprioritization phase are meant to inform
EPA’s decisions on (1) whether to
initiate the prioritization process on a
particular chemical substance, and (2)
once initiated, the proposed designation
of that chemical substance as either a
High-Priority Substances or LowPriority Substance.
I. Initiation of Prioritization
The prioritization process officially
begins, for purposes of triggering the
nine to twelve month statutory
timeframe, when EPA publishes a notice
in the Federal Register identifying a
chemical substance for prioritization.
The proposed rule also specifies that
EPA will publish the results of the
screening review in the Federal
Register, describing the information,
analysis and basis used to conduct that
review and providing in the docket
copies of relevant information not
otherwise protected as confidential
business information under TSCA
section 14. Publication of the notice in
the Federal Register also initiates a 90day public comment period. For each
chemical substance, EPA will open a
docket to facilitate receipt of public
comments and access to publicly
available information throughout this
process. Interested persons can submit
information regarding the results of the
screening review or any other
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information relevant to the chemical
substance. Of particular interest to EPA
will be information related to
‘‘conditions of use’’ that are missing
from the screening results. EPA will
consider all relevant information
received during this comment period.
Consistent with TSCA section
6(b)(1)(C)(iii), the proposed rule further
allows EPA to extend this initial public
comment period for up to 3 months to
receive and/or evaluate information
developed from a test order,
commensurate with EPA’s need for
additional time to receive and/or
evaluate this information. As a practical
matter, EPA is unlikely to often extend
this initial public comment, given EPA’s
intention to ensure that all or most of
the necessary information is available
before initiating the prioritization
process. Further, a three month window
would not often provide a sufficient
time to gather, let alone consider, new
test data for the prioritization process.
This is generally expected to be the case
even with the authority to more quickly
collect such information under the new
test order authority in TSCA section 4.
J. Proposed Priority Designation
Based on the results of the screening
review, relevant information received
from the public in the initial comment
period, and other information as
appropriate, EPA will propose to
designate the chemical substance as
either a High-Priority Substance or LowPriority Substance, as those terms are
defined in TSCA. In making this
proposed designation, as directed by the
statute, EPA will not consider costs or
other non-risk factors.
This proposed rule provides that EPA
will publish the proposed designation
in the Federal Register, along with an
identification of the information,
analysis and basis used to support a
proposed designation, in a form and
manner that EPA deems appropriate,
and provide a second comment period
of 90 days, during which time the
public may submit comments on EPA’s
proposed designation. EPA proposes to
use the same docket for this step of the
process. Because the supporting
documentation for a proposed HighPriority Substance designation is likely
to foreshadow what will go into a
scoping document for risk evaluation,
EPA will be particularly interested in
early comments on the accuracy of
scope-related information such as the
chemical’s ‘‘conditions of use.’’
In the event of insufficient
information at the proposed designation
step, EPA is proposing to designate a
chemical substance as a High-Priority
Substance. EPA expects this situation to
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occur infrequently based on its
application of the criteria and
considerations during the preprioritization phase. However, if for
some reason the information available to
EPA is insufficient to support a
proposed designation of the chemical
substance as a Low-Priority Substance,
including after any extension of the
initial public comment period,
consistent with the statute, the proposed
rule requires EPA to propose to
designate the chemical substance as a
High-Priority Substance. The statute
requires that the prioritization process
lead to one of two outcomes by the end
of the 12-month deadline: A HighPriority Substance designation or a LowPriority Substance designation. 15
U.S.C. 2605(b)(1)(B). There is no third
option to allow EPA to either require the
development of additional information
or otherwise toll this deadline. Further,
the statute specifically requires that a
Low-Priority Substance designation be
based on ‘‘information sufficient to
establish’’ that a chemical substance
meets the definition. 15 U.S.C.
2605(b)(1)(B)(ii). There is no comparable
statutory requirement for High-Priority
Substance designations. 15 U.S.C.
2605(b)(1)(B)(i). It is also relevant that
the effect of designating a chemical as
High-Priority Substance is that EPA
further evaluates the chemical
substance; by contrast, a Low-Priority
Substance designation is a final Agency
determination that no further evaluation
is warranted—a determination that
constitutes final agency action, subject
to judicial review. 15 U.S.C.
2618(a)(1)(C)(i).
The logical implication of this
statutory structure is that scientific
uncertainty in this process (including as
a result of insufficient information) is to
weigh in favor of a High-Priority
Substance designation, as it is merely an
interim step that ensures that the
chemical will be further evaluated.
EPA’s proposal would also ensure that
this process would not create any
incentives for parties to withhold
readily available information, or
inadvertently discourage the voluntary
generation of data, as could occur were
EPA to establish, for example, a default
designation to Low-Priority. As a
practical matter, however, EPA expects
this situation to occur infrequently,
based on its proposed criteria and
considerations that will generally
ensure that sufficient information is
available to conduct a risk evaluation
before initiating prioritization. Priority
designations, whether they were based
on sufficient information or a lack of
sufficient information, are neither an
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affirmation of risk nor safety. EPA
therefore recognizes that all priority
designations will need to be carefully
communicated to the public.
For proposed designations as LowPriority Substances, EPA is proposing to
require that all comments that could be
raised on the issues in the proposed
designation must be presented during
the comment period. Any issues not
raised will be considered to have been
waived, and may not form the basis for
an objection or challenge in any
subsequent administrative or judicial
proceeding. This is a well-established
principle of administrative law and
practice, e.g., Nuclear Energy Institute v.
EPA, 373 F.3d 1251, 1290–1291 (D.C.
Cir. 2004), and the need for such a
provision is reinforced by the statutory
deadlines under which EPA must
operate here. EPA is restricting this to
Low-Priority Substance designations, as
it is the last opportunity for public input
before EPA’s action becomes final, and
thus it is imperative that any issues are
shared during this public comment
period. By contrast, designation of a
chemical substance as a High-Priority
Substance is not final agency action.
The statute mandates additional
opportunities for public input during
the risk evaluation process, and EPA
does not consider it appropriate to
restrict the public’s ability to comment
during these subsequent processes
based on this early phase proceeding.
K. Final Priority Designation
After considering any additional
information collected during the
proposed designation step, as
appropriate, the last step in the
prioritization process is for EPA to
finalize its designation of a chemical
substance as either a High-Priority
Substance or a Low-Priority Substance.
The proposed rule specifies that EPA
will publish the priority designation in
the Federal Register, and will use the
same docket. Again, TSCA prohibits
costs or other non-risk factors from
being considered in this designation.
And, as with the proposed designation
step, if information available to EPA
remains insufficient to support the final
designation of the chemical substance as
a Low-Priority Substance, EPA will
finalize the designation as a HighPriority Substance. Although final HighPriority designations based on
insufficient information are unlikely for
all the reasons described in Unit III.J.,
such a designation would require EPA
to conduct a risk evaluation on that
substance, and to support the risk
evaluation with adequate information.
EPA would need to develop or require
development of the necessary
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information and complete the risk
evaluation within the 3-year statutory
deadline.
L. Repopulation of High-Priority
Substances
TSCA requires EPA to finalize a
designation for at least one new HighPriority Substance upon completion of a
risk evaluation for another chemical
substance, other than a risk evaluation
that was requested by a manufacturer.
Because the timing for the completion of
risk evaluation and/or the prioritization
process will be difficult to predict, EPA
intends to satisfy this 1-off-1-on
replacement obligation as follows: In the
notice published in the Federal Register
finalizing the designation of a new
High-Priority Substance, EPA will
identify the complete or near-complete
risk evaluation that the new HighPriority Substance will replace. So long
as the designation occurs within a
reasonable time before or after the
completion of the risk evaluation, this
will satisfy Congress’ intent while
avoiding unnecessary delay and the
logistical challenges that would be
associated with more perfectly aligning
a High-Priority Substance designation
with the completion of a risk evaluation.
M. Effect of Final Priority Designation
Final designation of a chemical
substance as a High-Priority Substance
requires EPA to immediately begin a
risk evaluation on that chemical
substance. It is important to note that
High-Priority Substance designation
does not mean that the Agency has
determined that the chemical substance
presents a risk to human health or the
environment—only that the Agency
intends to consider the chemical
substance for further risk review and
evaluation. A High-Priority Substance
designation is not a final agency action
and is not subject to judicial review or
review under the Congressional Review
Act (CRA), 5 U.S.C. 801 et seq.
Final designation of a chemical
substance as a Low-Priority Substance
means that a risk evaluation of the
chemical substance is not warranted at
the time, but does not preclude EPA
from later revising the designation, if
warranted. Notably, a Low-Priority
Substance designation is explicitly
subject to judicial review. 15 U.S.C.
2618(a)(1)(C).
N. Revision of Designation
TSCA provides that EPA may revise a
final designation of a chemical
substance from a Low-Priority
Substance to a High-Priority Substance
at any time based on information
available to the Agency. The proposed
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4833
rule outlines the process the Agency
will take to revise such a designation.
Specifically, EPA would (1) re-screen
the chemical substance incorporating
the relevant information, (2) re-initiate
the prioritization process and take
public comment, (3) re-propose a
priority designation and take public
comment, and (4) re-finalize the priority
designation. EPA will not revise a final
designation of a chemical substance
from High-Priority Substance to LowPriority Substance, but rather see the
risk evaluation process through to its
conclusion.
IV. References
The following is a listing of the
documents that are specifically
referenced in this document. The docket
includes these documents and other
information considered by EPA,
including documents that are referenced
within the documents that are included
in the docket, even if the referenced
document is not physically located in
the docket. For assistance in locating
these other documents, please consult
the technical person listed under FOR
FURTHER INFORMATION CONTACT.
1. EPA. TSCA Work Plan for Chemical
Assessments: 2014 Update. October
2014. Available online at: https://
www.epa.gov/sites/production/files/
2015-01/documents/tsca_work_plan_
chemicals_2014_update-final.pdf.
2. EPA. Framework for Metals Risk
Assessment. EPA 120/R–07/001. March
2007. Available online at: https://
www.epa.gov/sites/production/files/
2013-09/documents/metals-riskassessment-final.pdf.
3. EPA. Science Policy Council Handbook:
Risk Characterization. EPA/100/B–00/
002. December 2000. Available online at:
https://www.epa.gov/risk/riskcharacterization-handbook.
4. EPA. TSCA Work Plan Chemicals:
Methods Document. February 2012.
Available online at: https://
www.epa.gov/sites/production/files/
2014-03/documents/work_plan_
methods_document_web_final.pdf.
5. EPA. 2012 TSCA Work Plan Chemicals.
June 2012. Available online at: https://
www.epa.gov/sites/production/files/
2014-02/documents/work_plan_
chemicals_web_final.pdf.
6. EPA. Safer Chemical Ingredients List
(SCIL). Available online at: https://
www.epa.gov/saferchoice/saferingredients. See also Master Criteria,
September 2012, Version 2.1, available
online at: https://www.epa.gov/sites/
production/files/2013-12/documents/
dfe_master_criteria_safer_ingredients_
v2_1.pdf.
V. Statutory and Executive Order
Reviews
Additional information about these
statutes and Executive Orders can be
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found at https://www2.epa.gov/lawsregulations/laws-and-executive-orders.
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
This action is a significant regulatory
action that was submitted to the Office
of Management and Budget (OMB) for
review under Executive Orders 12866
(58 FR 51735, October 4, 1993) and
13563 (76 FR 3821, January 21, 2011).
Any changes made in response to OMB
recommendations have been
documented in the docket.
B. Paperwork Reduction Act (PRA)
This action does not contain any
information collection activities that
require approval under the PRA, 44
U.S.C. 3501 et seq. This rulemaking
addresses internal EPA operations and
procedures and does not impose any
requirements on the public.
C. Regulatory Flexibility Act (RFA)
I certify under section 605(b) of the
RFA, 5 U.S.C. 601 et seq., that this
action will not have a significant
economic impact on a substantial
number of small entities. This
rulemaking addresses internal EPA
operations and procedures and does not
impose any requirements on the public,
including small entities.
D. Unfunded Mandates Reform Act
(UMRA)
This action does not contain any
unfunded mandate as described in
UMRA, 2 U.S.C. 1531–1538, and does
not significantly or uniquely affect small
governments. The action imposes no
enforceable duty on any state, local or
tribal governments or the private sector.
E. Executive Order 13132: Federalism
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This action does not have federalism
implications as specified in Executive
Order 13132 (64 FR 43255, August 10,
1999). 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.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This action does not have tribal
implications as specified in Executive
Order 13175 (65 FR 67249, November 9,
2000). It will not have substantial direct
effects on one or more Indian tribes, on
the relationship between the Federal
Government and Indian tribes, or on the
distribution of power and
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responsibilities between the Federal
Government and Indian tribes. Thus,
Executive Order 13175 does not apply
to this action.
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
EPA interprets Executive Order 13045
(62 FR 19885, April 23, 1997) as
applying only to those regulatory
actions that concern environmental
health or safety risks that the EPA has
reason to believe may
disproportionately affect children, per
the definition of ‘‘covered regulatory
action’’ in section 2–202 of the
Executive Order. This action is not
subject to Executive Order 13045
because it does not concern an
environmental health risk or safety risk.
H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not a ‘‘significant
energy action’’ as defined in Executive
Order 13211 (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. This
rulemaking addresses internal EPA
operations and procedures and does not
impose any requirements on the public.
I. National Technology Transfer and
Advancement Act (NTTAA)
This rulemaking does not involve any
technical standards, and is therefore not
subject to considerations under NTTAA
section 12(d), 15 U.S.C. 272 note.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
This action does not establish an
environmental health or safety standard,
and is therefore not is not subject to
environmental justice considerations
under Executive Order 12898 (59 FR
7629, February 16, 1994). This
rulemaking addresses internal EPA
operations and procedures and does not
have any impact on human health or the
environment.
List of Subjects in 40 CFR Part 702
Environmental protection, Chemicals,
Chemical substances, Hazardous
substances, Health and safety,
Prioritization, Screening, Toxic
substances.
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Dated: December 27, 2016
Gina McCarthy,
Administrator.
Therefore, 40 CFR chapter I,
subchapter R, is proposed to be
amended as follows:
PART 702—[AMENDED]
1. The authority citation for part 702
is revised to read as follows:
■
Authority: 15 U.S.C. 2605 and 2619.
■
2. Add subpart A to read as follows:
PART 702—GENERAL PRACTICES
AND PROCEDURES
Subpart A—Procedures for Prioritization of
Chemical Substances for Risk Evaluation
702.1 General Provisions.
702.3 Definitions.
702.5 Considerations for Potential
Candidates for Prioritization.
702.7 Candidate Selection and Screening
Review.
702.9 Initiation of Prioritization Process.
702.11 Proposed Priority Designation.
702.13 FinaL Priority Designation.
702.15 Revision of Designation.
702.17 Effect of Designation as a LowPriority Substance.
702.19 Effect of Designation as a HighPriority Substance.
*
*
*
*
*
Authority: 15 U.S.C. 2605 and 2619.
Subpart A—Procedures for
Prioritization of Chemical Substances
for Risk Evaluation
§ 702.1
General Provisions.
(a) Purpose. This regulation
establishes the risk-based screening
process for designating chemical
substances as a High-Priority Substance
or a Low-Priority Substance for risk
evaluation as required under section
6(b) of the Toxic Substances Control
Act, as amended (15 U.S.C. 2605(b)).
(b) Scope of designations. EPA will
make priority designations pursuant to
these procedures for a chemical
substance, not for a specific condition or
conditions of use of a chemical
substance.
(c) Categories of chemical substances.
Nothing in this subpart shall be
interpreted as a limitation on EPA’s
authority under 15 U.S.C. 2625(c) to
take action, including the actions
contemplated in this subpart, on a
category of chemical substances.
(d) Prioritization timeframe. The
Agency will publish a final priority
designation for a chemical substance in
no fewer than 9 months and no longer
than 1 year following initiation of
prioritization pursuant to 40 CFR 702.9.
(e) Metals or metal compounds. In
identifying priorities for chemical
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substances that are metals or metal
compounds, EPA will, as appropriate,
refer to relevant considerations from the
Framework for Metals Assessment of the
Office of the Science Advisor, Risk
Assessment Forum, dated March 2007,
or a successor document that addresses
metals risk assessment and is peer
reviewed by the Science Advisory
Board.
(f) Applicability. These regulations do
not apply to any chemical substance for
which a manufacturer requests a risk
evaluation under TSCA section
6(b)(4)(C) (15 U.S.C. 2605(b)(4)(C)).
§ 702.3
Definitions.
For purposes of this subpart, the
following definitions apply:
Act means the Toxic Substances
Control Act, as amended (15 U.S.C.
2601 et seq.)
EPA means the U.S. Environmental
Protection Agency.
High-Priority Substance means a
chemical substance that EPA
determines, without consideration of
costs or other non-risk factors, may
present an unreasonable risk of injury to
health or the environment because of a
potential hazard and a potential route of
exposure under the conditions of use,
including an unreasonable risk to
potentially exposed or susceptible
subpopulations identified as relevant by
EPA.
Low-Priority Substance means a
chemical substance that EPA concludes,
based on information sufficient to
establish, without consideration of costs
or other non-risk factors, does not meet
the standard for a High-Priority
Substance.
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§ 702.5 Consideration of Potential
Candidates for Prioritization.
(a) Potential High-Priority Substance
Candidates. In identifying potential
candidates for High-Priority Substances,
EPA will generally consider whether
information available to the Agency
suggests there is hazard and exposure
under a condition or conditions of use,
and whether a risk evaluation would be
needed to determine whether there is an
unreasonable risk of injury to health or
the environment.
(b) Potential Low-Priority Substance
Candidates. In identifying potential
candidates for Low-Priority Substances,
EPA will generally consider whether
information available to the EPA
suggests such low hazard and/or
exposure under all conditions of use
that EPA is confident the chemical
substances does not present an
unreasonable risk of injury to health or
the environment, including an
unreasonable risk to potentially exposed
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or susceptible subpopulations identified
as relevant by EPA, even in the absence
of a risk evaluation.
(c) Exposure and Hazard
Considerations for Potential Candidates.
In identifying potential candidates for
prioritization, EPA will generally
evaluate whether or not the chemical
substance meets one or more of the
following exposure or hazard
considerations:
(1) Persistent, bioaccumulative, and
toxic;
(2) Used in children’s products;
(3) Used in consumer products;
(4) Detected in human and/or
ecological biomonitoring programs;
(5) Potentially of concern for
children’s health;
(6) High acute and chronic toxicity;
(7) Probable or known carcinogen;
(8) Neurotoxicity; or
(9) Other emerging exposure and
hazard concerns to human health or the
environment, as determined by the
Agency.
A chemical substance that meets one or
more of these criteria will generally be
considered as a potential candidate for
further consideration as a High-Priority
Substance. A chemical substance that
meets none of these criteria will
generally be considered as a potential
candidate for further consideration as a
Low-Priority Substance.
(d) Available Information and
Resources. EPA expects it will often be
difficult to timely require development
of necessary chemical information, and
receive, evaluate, and incorporate that
information into analyses, during the
prioritization and risk evaluation
processes, within the statutory
deadlines under the Act for
prioritization and risk evaluation at 15
U.S.C. 2605 (b)(1)(C) and (b)(4)(G).
Therefore, EPA will generally review
and analyze the information necessary
for both prioritization and risk
evaluation prior to initiating the
prioritization process for a chemical
substance pursuant to 40 CFR 702.9.
Specifically, in identifying potential
candidates for prioritization, EPA
expects to consider:
(1) The availability of information and
resources necessary and sufficient to
support a priority designation pursuant
to 40 CFR 702.11, a risk evaluation
pursuant to 40 CFR 702, subpart B, or
other such action as determined by the
Administrator; and
(2) The ability of EPA to timely
develop or require development of
information necessary and sufficient to
support a priority designation pursuant
to 40 CFR 702.11; a risk evaluation
pursuant to 40 CFR 702, subpart B; or
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4835
other such action as determined by the
Agency.
(e) Insufficient Information. In the
absence of sufficient information to
support a priority designation pursuant
to 40 CFR 702.11, a risk evaluation
pursuant to 40 CFR 702, subpart B, or
other such action as determined by the
Agency, EPA may use its authorities
under the Act, and other information
gathering authorities, to gather or
require the generation of the needed
information on a chemical substance
before initiating the prioritization
process for that chemical substance.
§ 702.7 Candidate Selection and Screening
Review.
(a) Preferences and TSCA Work Plan.
In selecting a candidate for
prioritization as a High-Priority
Substance, EPA will:
(1) Give preference to:
(A) Chemical substances that are
listed in the 2014 update of the TSCA
Work Plan for Chemical Assessments as
having a persistence and
bioaccumulation score of 3, and
(B) Chemical substances that are
listed in the 2014 update of the TSCA
Work Plan for Chemical Assessments
that are known human carcinogens and
have high acute and chronic toxicity;
and
(2) Identify a sufficient number of
candidates from the 2014 update of the
TSCA Work Plan for Chemical
Assessments to ensure that, at any given
time, at least 50 percent of risk
evaluations being conducted by EPA are
drawn from that list until all substances
on the list have been designated as
either a High-Priority Substance or LowPriority Substance pursuant to 40 CFR
702.13.
(b) General Objective. In selecting
candidates for a High-Priority Substance
designation, it is EPA’s general objective
to select those chemical substances with
the greatest hazard and exposure
potential first, considering available
information on the relative hazard and
exposure of potential candidates. EPA
may also consider the relative hazard
and exposure of a potential candidate’s
substitutes. EPA is not required to select
candidates or initiate prioritization
pursuant to 40 CFR 702.9 in any ranked
or hierarchical order.
(c) Screening Review. Following
selection of a candidate chemical
substance, EPA will generally use
available information to screen the
candidate chemical substance against
the following criteria and
considerations:
(1) The chemical substance’s hazard
and exposure potential;
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(2) The chemical substance’s
persistence and bioaccumulation;
(3) Potentially exposed or susceptible
subpopulations;
(4) Storage of the chemical substance
near significant sources of drinking
water;
(5) The chemical substance’s
conditions of use or significant changes
in conditions of use;
(6) The chemical substance’s
production volume or significant
changes in production volume; and
(7) Any other risk-based criteria
relevant to the designation of the
chemical substance’s priority, in EPA’s
discretion.
(d) Information sources. In
conducting the screening review in
paragraph (c) of this section, EPA
expects to consider sources of
information relevant to the listed
criteria, including, as appropriate,
sources for hazard and exposure data
listed in Appendices A and B of the
TSCA Work Plan Chemicals: Methods
Document (February 2012).
(e) The purpose of the preferences and
criteria in paragraph (a) of this section
and the screening review in paragraph
(c) of this section are to inform EPA’s
decision whether or not to initiate the
prioritization process pursuant to 40
CFR 702.9, and the proposed
designation of the chemical substance as
either a High-Priority Substance or a
Low-Priority Substance pursuant to 40
CFR 702.11.
(f) If, after the screening review in
paragraph (c) of this section, EPA
believes it will not have sufficient
information to support a proposed
priority designation pursuant to 40 CFR
702.11, a risk evaluation pursuant to 40
CFR 702, subpart B, or other such action
as determined by the Agency, EPA is
likely to use its authorities under the
Act, and other information gathering
authorities, to generate the needed
information before initiating
prioritization pursuant to 40 CFR 702.9.
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§ 702.9
Initiation of Prioritization Process.
(a) EPA generally expects to initiate
the prioritization process for a chemical
substance only when it believes that all
or most of the information necessary to
prioritize and perform a risk evaluation
on the substance already exists.
(b) EPA will initiate prioritization by
publishing a notice in the Federal
Register identifying a chemical
substance for prioritization and the
results of the screening review
conducted pursuant to 40 CFR 702.7(c).
(c) The prioritization timeframe in 40
CFR 702.1(d) begins upon EPA’s
publication of the notice described in
paragraph (b) of this section.
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(d) The results of the screening review
published pursuant to paragraph (b) of
this section will identify, in a form and
manner that EPA deems appropriate, the
information analysis and basis used in
conducting the screening process.
Subject to 15 U.S.C. 2613, copies of the
information will also be placed in a
public docket established for each
chemical substance.
(e) Publication of a notice in the
Federal Register pursuant to paragraph
(b) of this section will initiate a period
of 90 days during which interested
persons may submit relevant
information on that chemical substance.
Relevant information might include, but
is not limited to, any information
regarding the results of the screening
review conducted pursuant to 40 CFR
702.7(c), and any additional information
on the chemical substance that pertains
to the criteria and considerations at 40
CFR 702.7(c).
(f) EPA may, in its discretion, extend
the public comment period in paragraph
(b) of this section for up to three months
in order to receive or evaluate
information submitted under 15 U.S.C.
2603(a)(2)(B). The length of the
extension will be based upon EPA’s
assessment of the time necessary for
EPA to receive and/or evaluate
information submitted under 15 U.S.C.
2603(a)(2)(B).
§ 702.11
Proposed Priority Designation.
(a) Based on the results of the
screening review in 40 CFR 702.7(c),
relevant information received from the
public as described in 40 CFR 702.9(e),
and other information as appropriate
and in EPA’s discretion, EPA will
propose to designate the chemical
substance as either a High-Priority
Substance or Low-Priority Substance.
(b) EPA will not consider costs or
other non-risk factors in making a
proposed priority designation.
(c) If information available to EPA
remains insufficient to enable the
proposed designation of the chemical
substance as a Low-Priority Substance,
including after any extension of the
initial public comment period pursuant
to 40 CFR 702.9(f), EPA will propose to
designate the chemical substance as a
High-Priority Substance.
(d) EPA may propose to designate a
chemical substance as a High-Priority
Substance based on the proposed
conclusion that the chemical substance
satisfies the definition of High-Priority
Substance in 40 CFR 702.3 under any
one or more uses that the Agency
determines constitute conditions of use
as defined in 15 U.S.C. 2602. EPA will
propose to designate a chemical
substance as a Low-Priority Substance
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based only on the proposed conclusion
that the chemical substance satisfies the
definition of Low-Priority Substance in
40 CFR 702.3 under all uses that the
Agency determines constitute
conditions of use as defined in 15 U.S.C.
2602.
(e) EPA will publish the proposed
designation in the Federal Register,
along with an identification of the
information, analysis and basis used to
support a proposed designation, in a
form and manner that EPA deems
appropriate, and provide a comment
period of 90 days, during which time
the public may submit comment on
EPA’s proposed designation. EPA will
open a docket to facilitate receipt of
public comment.
(f) For chemical substances that EPA
proposes to designate as Low-Priority
Substances, EPA will specify in the
notice published pursuant to paragraph
(e) of this section that all comments that
could be raised on the issues in the
proposed designation must be presented
during this comment period. Any issues
not raised at this time will be
considered to have been waived, and
may not form the basis for an objection
or challenge in any subsequent
administrative or judicial proceeding.
§ 702.13
Final Priority Designation.
(a) After considering any additional
information collected from the proposed
designation process in 40 CFR 702.11,
as appropriate, EPA will finalize its
designation of a chemical substance as
either a High-Priority Substance or a
Low-Priority Substance.
(b) EPA will not consider costs or
other non-risk factors in making a final
priority designation.
(c) EPA will publish each final
priority designation in the Federal
Register.
(d) EPA will finalize a designation for
at least one High-Priority Substance for
each risk evaluation it completes, other
than a risk evaluation that was
requested by a manufacturer pursuant to
40 CFR 702, subpart B. The obligation
in 15 U.S.C. 2605(b)(3)(C) will be
satisfied by the designation of at least
one High-Priority Substance where such
designation specifies the risk evaluation
that the designation corresponds to, and
where the designation occurs within a
reasonable time before or after the
completion of the risk evaluation.
(e) If information available to EPA
remains insufficient to enable the final
designation of the chemical substance as
a Low-Priority Substance, EPA will
finalize the designation of the chemical
substance as a High-Priority Substance.
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§ 702.15
Revision of Designation.
EPA may revise a final designation of
chemical substance from Low-Priority to
High-Priority Substance at any time
based on information available to the
Agency. To revise such a designation,
EPA will re-screen the chemical
substance pursuant to 40 CFR 702.7(c),
re-initiate the prioritization process on
that chemical substance in accordance
with 40 CFR 702.9, propose a priority
designation pursuant to 40 CFR 702.11,
and finalize the priority designation
pursuant to 40 CFR 702.13. EPA will not
revise a final designation of a chemical
substance from a High-Priority
Substance designation to Low-Priority.
§ 702.17 Effect of Designation as a LowPriority Substance.
Designation of a chemical substance
as a Low-Priority Substance under 40
CFR 702.3 means that a risk evaluation
of the chemical substance is not
warranted at the time, but does not
preclude EPA from later revising the
designation pursuant to 40 CFR 702.15,
if warranted.
§ 702.19 Effect of Designation as a HighPriority Substance.
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Final designation of a chemical
substance as a High-Priority Substance
under 40 CFR 702.13 initiates a risk
evaluation pursuant to 40 CFR 702,
subpart B. Designation as a HighPriority Substance is not a final agency
VerDate Sep<11>2014
17:33 Jan 13, 2017
Jkt 241001
action and is not subject to judicial
review.
*
*
*
*
*
[FR Doc. 2017–00051 Filed 1–13–17; 8:45 am]
BILLING CODE 6560–50–P
4837
FOR FURTHER INFORMATION CONTACT:
Kristi Thornton, Consumer Policy
Division, Consumer and Governmental
Affairs Bureau, at (202) 418–2467 or
email: Kristi.Thornton@fcc.gov.
This is a
summary of the Commission’s
FEDERAL COMMUNICATIONS
document, Report No. 3066, released
COMMISSION
January 6, 2017. The full text of the
Petition is available for viewing and
47 CFR Part 64
copying at the FCC Reference
Information Center, 445 12th Street SW.,
[CG Docket No. 02–278; Report No. 3066]
Room CY–A257, Washington, DC 20554.
Petition for Reconsideration of Action
It also may be accessed online via the
in Rulemaking Proceeding
Commission’s Electronic Comment
Filing System at: https://www.fcc.gov/
AGENCY: Federal Communications
ecfs/filing/1217190700960/document/
Commission.
1217190700960fd71. The Commission
ACTION: Petition for reconsideration.
will not send a copy of this document
SUMMARY: A Petition for Reconsideration pursuant to the Congressional Review
Act, 5 U.S.C. 801(a)(1)(A), because this
(Petition) has been filed in the
document does not have an impact on
Commission’s rulemaking proceeding,
any rules of particular applicability.
Sarah E. Ducich and Mark W. Brennan
on behalf of Navient Corp., Joseph
Subject: In the Matter of Rules and
Popevis and Rich Benenson on behalf of Regulations Implementing the
Nelnet Servicing LLC, Rebecca Emily
Telephone Consumer Protection Act of
Rapp on behalf of Great Lakes Higher
1991, FCC 16–99, published at 81 FR
Education Corporation, Jason L.
80594, November 16, 2016, in CG
Swartley on behalf of Pennsylvania
Docket No. 02–278. This document is
Higher Education Assistance Agency,
being published pursuant to 47 CFR
and Winfield P. Crigler on behalf of
1.429(e). See also 47 CFR 1.4(b)(1) and
Student Loan Servicing Alliance.
1.429(f), (g).
DATES: Oppositions to the Petition must
Number of Petitions Filed: 1.
be filed on or before February 1, 2017.
Federal Communications Commission.
Replies to an opposition must be filed
Marlene H. Dortch,
on or before February 13, 2017.
Secretary.
ADDRESSES: Federal Communications
[FR Doc. 2017–00848 Filed 1–13–17; 8:45 am]
Commission, 445 12th Street SW.,
Washington, DC 20554.
BILLING CODE 6712–01–P
PO 00000
SUPPLEMENTARY INFORMATION:
Frm 00040
Fmt 4702
Sfmt 9990
E:\FR\FM\17JAP1.SGM
17JAP1
Agencies
[Federal Register Volume 82, Number 10 (Tuesday, January 17, 2017)]
[Proposed Rules]
[Pages 4825-4837]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2017-00051]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 702
[EPA-HQ-OPPT-2016-0636; FRL-9957-74]
RIN 2070-AK23
Procedures for Prioritization of Chemicals for Risk Evaluation
Under the Toxic Substances Control Act
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: As required under section 6(b)(1) of the Toxic Substances
Control Act (TSCA), EPA is proposing to establish a risk-based
screening process and criteria that EPA will use to identify chemical
substances as either High-Priority Substances for risk evaluation, or
Low-Priority Substances for which risk evaluations are not warranted at
the time. The proposed rule describes the processes for identifying
potential candidates for prioritization, selecting a candidate,
screening that candidate against certain criteria, formally initiating
the prioritization process, providing opportunities for public comment,
and proposing and finalizing designations of priority. Prioritization
is the initial step in a new process of existing chemical substance
review and risk management activity established under recent amendments
to TSCA.
DATES: Comments must be received on or before March 20, 2017.
ADDRESSES: Submit your comments, identified by docket identification
(ID) number EPA-HQ-OPPT-2016-0636, by one of the following methods:
Federal eRulemaking Portal: https://www.regulations.gov.
Follow the online instructions for submitting comments. Do not submit
electronically any information you consider to be Confidential Business
Information (CBI) or other information whose disclosure is restricted
by statute.
Mail: Document Control Office (7407M), Office of Pollution
Prevention and Toxics (OPPT), Environmental Protection Agency, 1200
Pennsylvania Ave. NW., Washington, DC 20460-0001.
Hand Delivery: To make special arrangements for hand
delivery or delivery of boxed information, please follow the
instructions at https://www.epa.gov/dockets/contacts.html. Additional
instructions on commenting or visiting the docket, along with more
information about dockets generally, is available at https://www.epa.gov/dockets.
FOR FURTHER INFORMATION CONTACT:
For technical information contact: Ryan Schmit, Immediate Office,
Office of Chemical Safety and Pollution Prevention, Environmental
Protection Agency, 1200 Pennsylvania Ave. NW., Washington, DC 20460-
0001; telephone number: (202) 564-0610; email address:
schmit.ryan@epa.gov.
For general information contact: The TSCA-Hotline, ABVI-Goodwill,
422 South Clinton Ave., Rochester, NY 14620; telephone number: (202)
554-1404; email address: TSCA-Hotline@epa.gov.
SUPPLEMENTARY INFORMATION:
I. Executive Summary
A. Does this action apply to me?
This proposed rule does not propose to establish any requirements
on persons or entities outside of the Agency. This action may, however,
be of interest to entities that are or may manufacture or import a
chemical substance regulated under TSCA (e.g., entities identified
under North American Industrial Classification System (NAICS) codes 325
and 324110). Since other entities may also be interested, the Agency
has not attempted to describe all the specific entities and
corresponding NAICS codes for entities that may be interested in or
affected by this action.
B. What action is the agency taking?
EPA is proposing to establish the internal processes and criteria
by which EPA will identify chemical substances as either High-Priority
Substances for risk evaluation, or Low-Priority Substances for which
risk evaluations are not warranted at the time.
C. Why is the agency taking this action?
This rulemaking is required by TSCA section 6(b)(1)(A).
Prioritization of chemical substances for further evaluation will
ensure that the Agency's limited resources are conserved for those
chemical substances most likely to present risks, thereby furthering
EPA's overall mission to protect health and the environment.
D. What is the agency's authority for taking this action?
EPA is proposing this rule pursuant to the authority in TSCA
section 6(b), 15 U.S.C. 2605(b). See also the discussion in Units II.A
and B.
E. What are the estimated incremental impacts of this action?
This is a proposed rule that would establish the processes by which
EPA intends to designate chemical substances as either High or Low-
Priority Substances for risk evaluation. It would not establish any
requirements on persons or entities outside of the Agency. EPA did not,
therefore, estimate potential incremental impacts from this action.
F. What should I consider as I prepare my comments for EPA?
1. Submitting CBI. Do not submit this information to EPA through
regulations.gov or email. Clearly mark the part or all of the
information that you claim to be CBI. For CBI information in a disk or
CD-ROM that
[[Page 4826]]
you mail to EPA, mark the outside of the disk or CD-ROM as CBI and then
identify electronically within the disk or CD-ROM the specific
information that is claimed as CBI. In addition to one complete version
of the comment that includes information claimed as CBI, a copy of the
comment that does not contain the information claimed as CBI must be
submitted for inclusion in the public docket. Information so marked
will not be disclosed except in accordance with procedures set forth in
40 CFR part 2.
2. Tips for preparing your comments. When preparing and submitting
your comments, see the commenting tips at https://www.epa.gov/dockets/comments.html.
II. Background
A. Recent Amendments to TSCA
On June 22, 2016, the President signed into law the ``Frank R.
Lautenberg Chemical Safety for the 21st Century Act'' (Pub. L. 114-
182), which imposed sweeping reforms to TSCA. The bill received broad
bipartisan support in the U.S. House of Representatives and Senate, and
its passage was heralded as the most significant update to an
environmental law in over 20 years. The amendments give EPA improved
authority to take actions to protect people and the environment from
the effects of dangerous chemical substances. Additional information on
the new law is available on EPA's Web site at https://www.epa.gov/assessing-and-managing-chemicals-under-tsca/frank-r-lautenberg-chemical-safety-21st-century-act.
When TSCA was originally enacted in 1976, it established an EPA-
administered health and safety review process for new chemical
substances prior to allowing their entry into the marketplace. However,
tens of thousands of chemical substances in existence at that time were
``grandfathered in'' with no requirement for EPA to ever evaluate their
risks to health or the environment. The absence of a review requirement
or deadlines for action, coupled with a burdensome statutory standard
for taking risk management action on existing chemical substances,
resulted in very few chemical substances ever being assessed for safety
by EPA, and even fewer subject to restrictions to address identified
risks.
One of the key features of the new law is the requirement that EPA
now systematically prioritize and assess existing chemical substances,
and manage identified risks. Through a combination of new authorities,
a risk-based safety standard, mandatory deadlines for action, and
minimum throughput requirements, TSCA effectively creates a
``pipeline'' by which EPA will conduct existing chemical substances
review and management. This new pipeline--from prioritization to risk
evaluation to risk management (when warranted)--is intended to drive
steady forward progress on the backlog of existing chemical substances
left largely unaddressed by the original law. Prioritization is the
initial step in this process.
B. Statutory Requirements for Prioritization
TSCA section 6(b)(1) requires EPA to establish, by rule, the
process and criteria for prioritizing chemical substances for risk
evaluation. Specifically, the law requires EPA to establish ``a risk-
based screening process, including criteria for designating chemical
substances as high-priority substances for risk evaluations or low-
priority substances for which risk evaluations are not warranted at the
time.'' TSCA sections 6(b)(1) through (3) provide further specificity
on both the process and criteria, including preferences for certain
chemical substances that EPA must apply, the procedural steps,
definitions of High-Priority Substances and Low-Priority Substances,
and screening criteria that EPA must consider in designating a chemical
substance as either High-Priority Substances or Low-Priority
Substances. The statutory requirements related to prioritization are
described in further detail in this unit.
1. Prioritization Steps. Based on TSCA sections 6(b)(1) through
(3), EPA is proposing to include four steps or phases in
prioritization: (1) Pre-Prioritization, (2) Initiation, (3) Proposed
Designation, and (4) Final Designation. During the Pre-Prioritization
phase, EPA is proposing to apply the statutory preferences in TSCA
section 6(b)(2), along with other criteria, to narrow the pool of
potential candidates, and identify a single chemical substance (or
category of chemical substances) to screen against the statutory
criteria in TSCA section 6(b)(1)(A). Aside from the statutory
preferences listed, the law does not direct or limit EPA in how it is
to ultimately select a chemical substance on which to initiate
prioritization, requiring only that the process be ``risk-based.'' At
the Initiation step, EPA must announce a candidate chemical substance
and give the public a 90-day comment period to submit relevant
information. 15 U.S.C. 2605(b)(1)(C)(i). At the Proposed Designation
step, EPA must propose to designate a chemical substance as either a
High-Priority Substance or a Low-Priority Substance, publish the
proposed designation and the information, analysis, and basis used to
make the designation, and take public comment a second time for 90
days. 15 U.S.C. 2605(b)(1)(C)(ii). At Final Designation, EPA must
either finalize a High-Priority Substance designation and initiate a
risk evaluation, or finalize a Low-Priority Substance designation in
which case it will not conduct a risk evaluation on the chemical
substance unless and until information leads EPA to revisit that
priority designation. 15 U.S.C. 2605(b)(3)(A) and (B).
2. Screening criteria and statutory preferences. The statute
defines a High-Priority Substance as one that the Administrator
concludes, without consideration of costs or other non-risk factors,
may present an unreasonable risk of injury to health or the environment
because of a potential hazard and a potential route of exposure under
the conditions of use, including an unreasonable risk to potentially
exposed or susceptible subpopulations identified as relevant by the
Administrator. 15 U.S.C. 2605(b)(1)(B)(i). Conversely, the law
specifies that a Low-Priority Substance is one that the Administrator
concludes, based on information sufficient to establish, without
consideration of costs or other non-risk factors, does not meet the
standard for designating a chemical substance a High-Priority
Substance. 15 U.S.C. 2605(b)(1)(B)(ii).
In designating the priority of a chemical substance, EPA must
screen a candidate chemical substance against certain criteria
specified in TSCA section 6(b)(1)(A). These include the hazard and
exposure potential of the chemical substance (e.g., persistence and
bioaccumulation, potentially exposed or susceptible subpopulations, and
storage near significant sources of drinking water), the conditions of
use or significant changes in the conditions of use of the chemical
substance, and the volume or significant changes in the volume of the
chemical substance manufactured or processed. EPA interprets
``significant changes in'' conditions of use to have relevance
primarily in the context of revising a priority designation. With
respect to an initial prioritization decision, any changes in use that
have occurred in the past would already be captured by the concept of
``conditions of use,'' as defined in TSCA section 3.
[[Page 4827]]
The results of this screen will help inform EPA's proposed priority
designation. However, given that the statutory deadlines are triggered
at the initiation of prioritization, and that EPA will want to have a
good understanding of the chemical substance before triggering those
deadlines, EPA will consider these screening criteria earlier in the
process. As discussed in more detail in Unit III., EPA is therefore
proposing to include the screening review in the rule as part of the
pre-prioritization phase.
In designating High-Priority Substances, EPA is to give preference
to chemical substances that are listed in the 2014 Update of the TSCA
Work Plan for Chemical Assessments (Ref. 1) that: (1) Have persistence
and bioaccumulation scores of 3; and (2) are known human carcinogens
and have high acute and chronic toxicity. 15 U.S.C. 2605(b)(2)(D). The
law further requires that 50% of all ongoing risk evaluations be drawn
from the 2014 Update to the TSCA Work Plan for Chemical Assessments,
meaning that, at least at the outset of the program, EPA will need to
draw at least 50% of High-Priority Substance designations from the same
list. 15 U.S.C. 2605(b)(2)(B).
3. Metals and metal compounds. When prioritizing metals or metal
compounds, EPA must use the March 2007 Framework for Metals Risk
Assessment of the Office of the Science Advisor (Ref. 2) (or a
successor document that addresses appropriate considerations for
conducting a risk assessment on a metal or metal compound and is peer
reviewed by the Science Advisory Board). 15 U.S.C. 2605(b)(2)(E).
However, during the prioritization process, EPA will not be conducting
chemical risk assessments; and, consequently, much of this guidance
will not be directly relevant. EPA interprets this provision to ensure
that the analysis and considerations during the prioritization process
take into account the special attributes and behaviors of metals and
metal compounds that are relevant to judgments of risk. For example,
this might include consideration of the document's Key Principles that
differentiate inorganic metals and metal compounds from organic and
organometallic compounds, and their unique attributes, properties,
issues, and processes. Because EPA will not conduct risk assessments on
metals or metal compounds for purposes of prioritization, EPA will not
refer to sections that provide guidance on how to incorporate the Key
Principles into risk assessments.
4. Timeframe. TSCA requires that the prioritization process last
between nine and twelve months. 15 U.S.C. 2605(b)(1)(C). This timeframe
takes on particular significance, given that the statute does not
authorize EPA to ``pause'' or delay the prioritization once it has been
initiated, and that a final High-Priority Substance designation results
in the chemical substance moving immediately into a risk evaluation
process that must be generally completed within three years. 15 U.S.C.
2605(b)(4)(G).
5. Opportunities for public participation. As already mentioned,
TSCA requires EPA to provide two 90-day public comment periods during
prioritization--one following initiation, and a second following a
proposed designation. 15 U.S.C. 2605(b)(1)(C)(i) and (ii). TSCA further
requires that EPA include a process for extending the comment deadline
for up to three months in order to receive or evaluate information
coming from a TSCA section 4 test order. 15 U.S.C. 2605(b)(1)(C)(iii).
These public comment periods, coupled with the nine month minimum
timeframe for prioritization, ensure that the public will be on notice
of EPA's intention to further evaluate a chemical's risks and will have
opportunity to engage early in the process before the risk evaluation
has started.
6. Default to High-Priority Substance Designation. If, after
prioritization has been initiated, the public has been given an
opportunity to submit relevant information, and EPA has extended the
comment period pursuant to TSCA section 6(b)(1)(C)(iii) in order to
receive or evaluate additional information, EPA determines that the
available information is insufficient to enable the designation of the
chemical substance as a Low-Priority Substance, the statute requires
EPA to propose a High-Priority Substance designation. 15 U.S.C.
2605(b)(1)(C)(iii). Based in part on this provision, and as discussed
further in Unit III, EPA is proposing to require a default-to-high in
all cases in which insufficient information exists to designate the
chemical as a Low-Priority Substance at both the proposed and final
designation.
7. Initial ten chemicals for risk evaluation. TSCA requires EPA to,
within six months of enactment, ensure that risk evaluations are being
conducted on ten chemical substances drawn from the 2014 update of the
TSCA Work Plan for Chemical Assessments, and to publish a list of those
chemical substances during that same period. 15 U.S.C. 2605(b)(2)(A).
The initial ten chemical substances are not subject to the
prioritization process or the procedures in this rule. However,
completion of these risk evaluations triggers the ongoing designation
requirement discussed in Unit II.B.8.
8. Ongoing designations. Upon completion of a risk evaluation
(other than those requested by a manufacturer pursuant to TSCA section
6(b)(4)(C)(ii)), EPA must designate at least one additional High-
Priority Substance to take its place. 15 U.S.C. 2605(b)(2)(C). Because
designation as a High-Priority Substance results in the chemical
substance moving immediately to risk evaluation, this provision
prevents the number of existing chemical substances undergoing risk
evaluation from ever decreasing over time. In addition, EPA must
designate at least twenty chemical substances as High-Priority
Substances by three and one half years after enactment, effectively
doubling the number of chemical substances in the review pipeline. 15
U.S.C. 2605(b)(2)(B). The statute also requires that at least twenty
chemical substances be designated as Low-Priority Substances by three
and one half years after enactment, but without a comparable
requirement to continue designating additional Low-Priority Substances
after that. 15 U.S.C. 2605(b)(2)(B), (b)(3)(C). Although EPA must
continue to prioritize and evaluate chemical substances ``at a pace
consistent with the ability of the Administrator to complete risk
evaluations in accordance with the deadlines,'' this provision does not
modify the minimum throughput or other ongoing designation requirements
for High-Priority Substances. 15 U.S.C. 2605(b)(2)(C). It does,
however, suggest that EPA must have adequate resources should EPA plan
to designate more than twenty chemical substances as High-Priority
Substances at any given time.
9. Revision of designation. TSCA allows the Administrator to revise
the designation of a Low-Priority Substance to a High-Priority
Substance ``based on information made available to the Administrator.''
15 U.S.C. 2605(b)(3)(B). This provision does not restrict the basis for
a revision to the discovery or receipt of new information. For example,
EPA could also justify a revision based on information that was
available but was not considered at the time of the original
prioritization decision, or information that was considered but which
EPA now views differently as a result of changes in scientific
understanding (e.g., changes in scientific understanding of how a
chemical can enter or interact with the human body).
10. Other relevant statutory requirements. TSCA imposes new
[[Page 4828]]
requirements on EPA in a number of different areas that EPA is not
proposing to incorporate or otherwise address in this proposed rule.
For example, amendments to TSCA section 4 require EPA to ``. . . reduce
and replace, to the extent practicable, [. . .] the use of vertebrate
animals in the testing of chemical substances . . .'' and to develop a
strategic plan to promote such alternative test methods. 15 U.S.C.
2603(h). Likewise, TSCA section 26 requires, to the extent that EPA
makes a decision based on science under TSCA sections 4, 5, or 6, that
EPA use certain scientific standards and base those decisions on the
weight of the scientific evidence. 15 U.S.C. 2625(h) and (i). While
these requirements are relevant to the prioritization of chemical
substances, EPA is not obliged to include them in this proposed rule.
By their express terms, these statutory requirements apply to EPA's
decisions under TSCA section 6, without the need for regulatory action.
Moreover, in contrast to TSCA section 6, Congress has not directed EPA
to implement these other requirements ``by rule;'' it is well-
established that where Congress has declined to require rulemaking, the
implementing agency has complete discretion to determine the
appropriate method by which to implement those provisions. E.g., United
States v. Storer Broadcasting Co., 351 U.S. 192 (1956).
A number of stakeholders raised questions as to whether EPA should
define a number of important terms in this rule (e.g., ``best available
science'', ``weight-of-the-evidence'', ``sufficiency of information'',
``unreasonable risk'', and ``reasonably available information''). Many
of the terms used in the proposed rule are not novel concepts and are
already in use, and their meaning is discussed extensively in existing
Agency guidance. For example, extensive descriptions for the phrases
``best available science'', ``weight-of-the-evidence'', and
``sufficiency of information'' can be found in EPA's Risk
Characterization Handbook (Ref. 3), and in other existing Agency
guidance.
EPA believes further defining these and other terms in the proposed
rule is unnecessary and ultimately problematic. These terms have and
will continue to evolve with changing scientific methods and
innovation. Codifying specific definitions for these phrases in this
rule may inhibit the flexibility and responsiveness of the Agency to
quickly adapt to and implement changing science. The Agency intends to
use existing guidance definitions and to update definitions and
guidance as necessary.
While EPA is seeking public comment on all aspects of this proposed
rule, the Agency is specifically requesting public input on this issue.
The Agency welcomes public comments regarding the pros and cons of
codifying these or other definitions and/or approaches for these or any
other terms. EPA encourages commenters to suggest alternative
definitions the Agency should consider for codification in this
procedural rule. Please explain your views as clearly as possible,
providing specific examples to illustrate your concerns and suggest
alternate wording, where applicable.
C. Prioritization Under the 2012 TSCA Work Plan Methodology
Prioritization of chemical substances for review is not a novel
concept for the Agency. In 2012, EPA released the TSCA Work Plan
Chemicals: Methods Document in which EPA described the process the
Agency intended to use to identify potential candidate chemical
substances for near-term review and assessment under TSCA (Ref. 4). EPA
also published an initial list of TSCA Work Plan chemicals identified
for further assessment under TSCA as part of its chemical safety
program in 2012 (Ref. 5), and an updated list of chemical substances
for further assessment in 2014 (Ref. 1). The process for identifying
these chemical substances was based on a combination of hazard,
exposure, and persistence and bioaccumulation characteristics.
Congress expressly recognized the validity of EPA's existing
prioritization methodology for the TSCA Work Plan. For example, the law
requires that EPA give certain preferences to chemical substances
listed on the 2014 Update to the TSCA Work Plan. 15 U.S.C.
2605(b)(2)(D). Moreover, the law requires that at least 50 percent of
all ongoing risk evaluations be drawn from the 2014 Update to the TSCA
Work Plan. 15 U.S.C. 2605(b)(2)(B). The statutory screening criteria in
TSCA section 6(b)(1)(A) also significantly overlaps with the
considerations in the Work Plan methodology (e.g., persistence,
bioaccumulation, toxicity, carcinogenicity, etc.).
However, there are a number of key differences between EPA's TSCA
Work Plan process and the prioritization process that TSCA now
requires. First, the Work Plan process involved culling through
thousands of chemical substances to create a list that EPA could, over
time and without prescribed deadlines, focus its limited resources on.
The TSCA Work Plan did not require EPA to assess listed chemical
substances, and included no deadlines for completing risk assessments
or addressing identified risks. Prioritization under this proposed rule
will involve a similar culling, but upon designating a chemical
substance as a High-Priority Substance, the Agency must start a risk
evaluation, and generally complete that evaluation within a specified
amount of time. If EPA determines in the risk evaluation that a
chemical substance presents an unreasonable risk of injury to health or
the environment, EPA must also initiate a risk management rulemaking
subject to statutory deadlines. 15 U.S.C. 2605(c). As such, EPA will
need to be judicious in selecting the chemical substances that go into
prioritization.
Further, while chemical substances listed on the TSCA Work Plan
were likely to be well-characterized for hazard and have at least some
information indicating potential exposure, Work Plan chemical substance
assessments have generally focused on specific chemical uses. Given the
statutory deadlines, EPA generally intends to ensure it has a more
complete set of data upfront that would allow EPA to evaluate a
chemical substance under all conditions of use (a broader scope) within
the statutory deadlines. For chemical substances with insufficient
information to conduct a risk evaluation, EPA generally expects to
pursue a significant amount of data gathering before initiating
prioritization.
Finally, the TSCA Work Plan process focused solely on identifying
potential high risk chemical substances for further review. Because the
statute also requires the identification of Low-Priority Substances--
those chemical substances that EPA has determined, based on sufficient
evidence, do not warrant further review at the time--EPA will need to
undertake new and different analyses than it has done to date under the
TSCA Work Plan.
While EPA has drawn from the TSCA Work Plan methodology and EPA's
experience in implementing that process in developing this proposed
rule, EPA is proposing to tailor the process for prioritization to the
specific requirements in the new statute.
D. Stakeholder Involvement
On August 10, 2016, EPA held a one day public meeting to hear from
stakeholders to better understand their viewpoints on the development
of the prioritization rule. The meeting began with a presentation from
EPA on how the Agency has prioritized chemicals for further review
under the TSCA Work Plan methodology. The remainder of the day was
reserved for public comment. Commenters had approximately four
[[Page 4829]]
minutes to present their comments orally and there was a total of 28
oral comments on the prioritization rule. Further information is
available on EPA's Web site at https://www.epa.gov/assessing-and-managing-chemicals-under-tsca/meetings-and-webinars-amended-toxic-substances-control.
Stakeholders were also able to provide written comments. EPA
received 50 written comments on the prioritization rule, although many
of those who presented orally also submitted written versions as well.
These comments and a transcript of the meeting are accessible in the
meeting's docket, identified by Docket ID No. EPA-HQ-OPPT-2016-0399,
available online at https://www.regulations.gov/.
The commenters included representatives from industry,
environmental groups, academics, private citizens, trade associations,
and health care representatives, and provided a diversity of
perspectives. Overall, there was a general expression of support for
the new law and EPA's inclusive approach to implementation to date.
Most groups agreed that the prioritization rule had the potential to
increase transparency in EPA's chemical substance review and management
process, and urged the Agency to work towards this goal.
A number of commenters suggested codifying specific details in the
rule, such as a system for scoring and ranking chemical substances; a
listing of the specific hazard and exposure information upon which EPA
will base prioritization decisions; and definitions of terms referenced
in the statute like ``weight of evidence'' and ``best available
science.'' Others encouraged EPA to keep the rules focused on a
framework for general process, to retain Agency discretion where
appropriate, and to reserve specific scientific considerations for
Agency guidance.
EPA considered all of these comments in the development of this
proposed rule, and welcomes additional feedback from stakeholders on
the Agency's proposed process for chemical substance prioritization as
presented in this document.
III. Summary of Proposed Rule
This proposed rule incorporates all of the elements required by
statute, but also supplements those requirements with additional
criteria the Agency expects to consider, some clarifications for
greater transparency, and additional procedural steps to ensure
effective implementation. Specific components of the approach are
discussed in this unit. EPA requests comments on all aspects of this
proposed rulemaking.
A. Policy Objective
The prioritization process under TSCA is the principal gateway to
risk evaluation. EPA is ultimately making a judgment as to whether or
not a particular chemical substance warrants further assessment. As a
general matter, the overall objective of the process should be to guide
the Agency towards identifying the High-Priority Substances that have
the greatest hazard and exposure potential first. EPA may also consider
the relative hazard and exposure of a potential candidate's likely
substitute(s) in order to avoid moving the market to a chemical
substance of equal or greater risks. However, the prioritization
process is not intended to be an exact scoring or ranking exercise and
EPA is not proposing such a system in this rule. The precise order in
which EPA identifies High-Priority Substances (all of which must meet
the same statutory standard) should not be allowed to slow the Agency's
progress towards fully evaluating the risks from those chemical
substances. Further, the level of analysis necessary to support an
exact ranking system is not appropriate at the prioritization stage,
where the sole outcome is a decision on whether EPA will further
evaluate the chemical substance. EPA intends to conserve its resources
and the Agency's deeper analytic efforts for the actual risk
evaluation. This policy objective is stated directly in the proposed
rule.
Low-Priority Substance designations serve some of the same policy
objectives. Although the statute does not require EPA to designate more
than twenty Low-Priority Substances, doing so ensures that chemical
substances with clearly low hazard and exposure potential are taken out
of consideration for further assessment, thereby conserving resources
for the chemical substances with the greatest potential risks. There is
also value in identifying Low-Priority Substances as part of this
process, as it gives the public notice of chemical substances for which
potential risks are likely low or nonexistent, and industry some
insight into which chemical substances are likely not to be regulated
under TSCA.
B. Scope of Designations
EPA will designate the priority of a ``chemical substance,'' as a
whole, under this established process, and will not limit its
designation to a specific use or subset of uses of a chemical
substance. EPA is proposing this in response to clear statutory
directives: The relevant provisions of TSCA section 6 repeatedly refer
to both the designation and evaluation of ``chemical substances'' under
the ``conditions of use.'' ``Conditions of use'' are broadly defined as
``the circumstances, as determined by the Administrator, under which a
chemical substance is intended, known, or reasonably foreseen to be
manufactured, processed, distributed in commerce, used, or disposed
of.'' 15 U.S.C. 2602.
Although some commenters at the public meeting suggested that the
prioritization process should allow EPA to designate a specific use of
a chemical substance as a High-Priority Substance or a Low-Priority
Substance, EPA does not interpret the statute to support such an
interpretation. To the contrary, the addition of the phrase
``conditions of use'' (emphasis added) was intended to move the Agency
away from its past practice of assessing only narrow uses of a chemical
substance, towards a comprehensive approach to chemical substance
management. While EPA clearly retains some discretion in determining
those conditions of use, as a matter of law, EPA considers that it
would be an abuse of that discretion to simply disregard known,
intended, or reasonably foreseen uses in its analyses.
C. Timeframe
As discussed in Unit II., TSCA section 6(b)(1)(C) requires that the
prioritization process last between nine and twelve months. EPA is
proposing in this rule that initiation of the prioritization begins
upon publication of a notice in the Federal Register that identifies a
chemical substance for prioritization and provides the results of the
screening review. The process is complete upon publication of a notice
in the Federal Register announcing a final priority designation.
Accordingly, the proposed rule specifies that the process--from
initiation to final designation--shall last between 9 and 12 months.
This timeframe serves dual purposes. The minimum 9-month timeframe
ensures that the general public; potentially-affected industries;
state, tribal and local governments; environmental and health non-
governmental organizations; and others have ample notice of upcoming
federal action on a given chemical substance, and opportunity to engage
with EPA early in the process. The 12-month maximum timeframe, coupled
with the default-to-high provision discussed later, keeps the existing
chemical substances review pipeline in a forward motion, and prevents
EPA from getting mired in analysis before ever reaching the risk
evaluation step.
[[Page 4830]]
D. Categories of Chemical Substances
TSCA section 26 provides EPA with authority to take action on
categories of chemical substances. 15 U.S.C. 2625(c). ``Category of
Chemical Substances'' is defined at 15 U.S.C. 2625(c)(2)(A). Although
the proposed rule most often references ``chemical substances,'' EPA is
also proposing to include a clear statement in the regulation that
nothing in the proposed rule shall be construed as a limitation on
EPA's authority to take action with respect to categories of chemical
substances, and that, where appropriate, EPA can prioritize and
evaluate categories of chemical substances.
E. Chemicals Subject to Prioritization
Generally, all chemical substances listed on the TSCA Inventory are
subject to prioritization. TSCA contemplates that, over time, all
chemical substances on the TSCA Inventory will be prioritized into
either High- or Low-Priority Substances, and that all High-Priority
Substances will be evaluated. EPA notes that chemical substances newly
added to the TSCA Inventory following EPA's completion of pre-
manufacture review under section 5 of TSCA (15 U.S.C. 2604) are also
candidates for prioritization, although EPA expects that such chemical
substances are not likely to be High-Priority candidates in light of
the risk-related determination that the Agency must make pursuant to
TSCA section 5(a)(3).
TSCA further requires EPA to go through a separate process of
determining which chemical substances on the TSCA Inventory are still
actively being manufactured, and EPA has initiated a separate
rulemaking for that purpose (RIN 2070-AK24). This distinction will
inform EPA's exposure judgments during the prioritization process.
However, there is nothing in TSCA that prohibits EPA from initiating
the prioritization process on an ``inactive'' chemical substance and
ultimately designating that chemical substance as either a High-
Priority Substances (e.g., if exposures of concern arise from ongoing
uses) or Low-Priority Substance.
F. Pre-Prioritization Considerations
As discussed earlier, TSCA requires that EPA establish a process,
including criteria for designating a chemical substance as either a
High-Priority Substances or Low-Priority Substance. 15 U.S.C.
2605(b)(1). Aside from the statutory preferences for chemical
substances on the 2014 Update to the TSCA Work Plan (Ref. 1), the
statute leaves EPA with broad discretion to choose which chemical
substance to put into that process. Accordingly, this proposed rule
includes a discussion of the criteria EPA expects to use to cull
through the chemical substances on the TSCA Inventory. These include
criteria that will be used to identify potential candidates for High-
Priority Substances or Low-Priority Substances, and that describe how
the extent of available information on potential candidates will affect
whether they are selected for prioritization.
For example, in identifying potential candidates for High-Priority
Substance designations, EPA is proposing to seek to identify chemical
substances where available information suggests that the chemical
substance may present a hazard and that exposure is present under ``one
or more conditions of use,'' but where an ``unreasonable risk''
determination cannot be made without a more extensive or complete
assessment in a risk evaluation. EPA interprets the statutory
definition of a High-Priority Substance (``. . . may present an
unreasonable risk [. . .] because of a potential hazard and a potential
route of exposure . . .'') to set a fairly low bar, and EPA expects
that a large number of chemical substances will meet this definition.
Although EPA will prioritize a ``chemical substance'' as a whole, EPA
may base its identification of a potential candidate as a High-Priority
Substance, and ultimately the proposed designation, on a single
condition of use, provided the hazard and exposure associated with that
single use support such a designation. This proposal is based on the
statutory definition of a High-Priority Substance, which is clear that
the standard for the chemical as a whole can be met based on a single
condition of use (``. . . because of a potential hazard and a potential
route of exposure . . .'').
Conversely, in identifying potential candidates for Low-Priority
Substance designation, EPA is proposing that it will seek to identify
chemical substances where the information indicates that hazard and
exposure potential for ``all conditions of use'' are so low that EPA
can confidently set that chemical substance aside without doing further
evaluation. By comparison, then, TSCA's definition of Low-Priority
Substance (``. . . based on sufficient information, such substance does
not meet the standard for [. . .] a high-priority substance . . .'') is
fairly rigorous, and effectively requires EPA to determine that under
no condition of use does the chemical meet the High-Priority Substance
standard. Consequently, EPA expects it will be more difficult to
support such designations. Unlike High-Priority Substances, EPA will
not be able to designate a chemical substance as a Low-Priority
Substance without first looking at all of the conditions of use. While
not determinative, EPA believes that its Safer Chemicals Ingredients
List (SCIL) (Ref. 6) will be a good starting point for identifying
potential candidates for Low-Priority Substance designations.
EPA is also proposing to include the following list of additional
exposure and hazard considerations that can be used to narrow the field
of potential candidates: (1) Persistent, bioaccumulative, and toxic;
(2) Used in children's products; (3) Used in consumer products; (4)
Detected in human and/or ecological biomonitoring programs; (5)
Potentially of concern for children's health; (6) High acute and
chronic toxicity; (7) Probable or known carcinogen; (8) Neurotoxicity;
or (9) Other emerging exposure and hazard concerns to human health or
the environment, as determined by the Agency. These criteria are drawn
from EPA's 2012 TSCA Work Plan methodology (Ref. 4), which, as
discussed earlier, was the process EPA had been using to prioritize
chemical substances for assessment under TSCA. EPA will evaluate one or
more of these nine considerations, and chemical substances that meet
one or more of these criteria may be identified as potential candidates
for High-Priority Substance designations. For example, if a chemical
substance is highly toxic and used in consumer products, EPA may wish
to consider that chemical substance as a potential High-Priority
Substance candidate. EPA may also choose to identify potential
candidates based on other criteria that suggest the chemical substance
may otherwise present a human health or environmental concern, as
contemplated in the ``catch-all'' provision (9). The fact that a
chemical substance meets one of these criteria is not determinative of
an outcome, including whether or not EPA will select the chemical
substance to go into the prioritization process and/or the priority
designation that the chemical substance will ultimately receive.
Conversely, chemical substances that meet none of these criteria may be
good potential candidates for Low-Priority Substance designation. The
considerations are intended to serve as a general guide for the Agency,
based on EPA's current understanding of important considerations
regarding
[[Page 4831]]
potential chemical risk. It should also be noted that while these
considerations are drawn from EPA's 2012 Work Plan methodology (Ref.
4), EPA will apply them differently for prioritization. In the TSCA
Work Plan context, only chemical substances that met these initial
criteria were eligible for listing on Work Plan. For purposes of
prioritization under TSCA, the considerations do not determine
eligibility, but rather are designed to help EPA to narrow its focus.
G. Information Availability
Another key consideration in the pre-prioritization phase is the
existence and availability of risk-related information on a candidate
or potential candidate chemical substance. Because EPA must complete
its prioritization process within 12 months once prioritization has
been initiated for a chemical substance, immediately initiate a risk
evaluation for High-Priority Substance, and complete the risk
evaluation within three years of initiation, EPA cannot assume that it
will be able to require the generation of critical information during
these time frames. Furthermore, the statute does not grant EPA the
discretion to significantly delay either of these processes, pending
development of information. Consequently, prior to initiating the
prioritization process for a chemical substance, EPA will generally
review the available hazard and exposure-related information, and
evaluate whether that information would be sufficient to allow EPA to
complete both prioritization and risk evaluation processes. As part of
such an evaluation, EPA expects to consider the quality, objectivity,
utility, and integrity of the available information. To the extent the
information is not currently available or is insufficient, EPA will
determine whether or not information can be developed and collected,
reviewed and incorporated into analyses and decisions in a timely
manner. The proposed rule makes it clear that sufficiency of available
information is likely to be a crucial factor in the selection of the
chemical substances that EPA chooses to put into the prioritization
process.
As noted, if information gaps are identified during the
prioritization or risk evaluation processes, EPA expects that it could
be difficult to require the development of necessary chemical substance
information, and receive, evaluate, and incorporate that information
into analyses and decisions within the statutory timeframes. Tests
necessary for risk evaluation, for example, could take months or years
to develop and execute, plus additional time for EPA to issue the order
or rule, and to collect, review and incorporate the new information. To
avoid such a scenario, EPA believes that it will need to do a
significant amount of upfront data gathering and review. This approach
ensures that EPA stays on track to meet relevant statutory deadlines--
particularly those for risk evaluation.
The proposed rule makes clear that EPA generally expects to use
this new authority, as appropriate and necessary, to gather the
requisite information prior to initiating prioritization. This could
include, as appropriate, TSCA information collection, testing, and
subpoena authorities, including those under TSCA sections 4, 8, and
11(c), to develop needed information.
Given the importance of ensuring that sufficient information is
available to conduct the prioritization and risk evaluation processes,
EPA is proposing to include this consideration during the earliest
stage in the process: During the identification of potential
candidates. However, this criterion remains relevant even after EPA has
selected a candidate and screened that chemical substance against the
statutory criteria in TSCA section 6(b)(1)(A). Thus, if at any time
prior to the publication of a notice in the Federal Register initiating
prioritization, EPA determines that more information will be necessary
to support a prioritization designation or a subsequent risk
evaluation, EPA can choose not to initiate prioritization for that
chemical substance pending development of additional information.
H. Selection and Screening of a Candidate Chemical Substance
As noted in Unit II., TSCA requires that EPA give preference to
chemical substances listed in the 2014 update of the TSCA Work Plan for
Chemical Assessments that (1) have a Persistence and Bioaccumulation
Score of 3; and (2) are known human carcinogens and have high acute and
chronic toxicity. TSCA section 6(b)(2)(B) further requires that 50
percent of all ongoing risk evaluations be drawn from the 2014 Update
to the TSCA Work Plan for Chemical Assessments, meaning that EPA will
need to draw at least 50 percent of High-Priority Substance candidates
from the same list. By operation of the statute, TSCA requires that all
TSCA Work Plan chemical substances eventually be prioritized. However,
it is premature to presume that those chemical substances will
necessarily be prioritized as High-Priority Substances, or that EPA
would find unreasonable risk.
Aside from these statutory preferences, however, TSCA does not
limit how EPA must ultimately select a candidate chemical substance to
put into the prioritization process. EPA is proposing that it will
select a candidate--for either High-Priority Substances or Low-Priority
Substance--based on the policy objectives described in Unit III.A. and
the pre-prioritization considerations described in Unit III. F. and G.
The development of the proposed rule, including these policy
objectives, considerations and criteria, was informed by EPA's
experience implementing the 2012 TSCA Work Plan methodology, which has
been the Agency's primary tool for identifying candidate chemical
substances for further assessment under TSCA. In addition, EPA fully
recognizes the important role that stakeholders can play in helping the
Agency to identify candidates for prioritization or to better
understand the unique uses or characteristics of a particular chemical.
EPA continues to welcome this type of engagement and dialogue early in
the process, including during the pre-prioritization phase. While the
proposed rule provides multiple opportunities for public feedback
during the prioritization process, EPA is requesting comment on whether
and how EPA should solicit additional input at the pre-prioritization
phase. Further, given EPA's objective to avoid simply moving the market
to substitute chemical substances of equal or greater risks, EPA
requests comment on whether and how information on the availability of
chemical substitutes should be taken into account during this phase of
the prioritization process.
Once a single candidate chemical substance (or category of chemical
substances) is selected, EPA will screen the selected candidate against
the specific criteria and considerations in TSCA section 6(b)(1)(A).
Those criteria and considerations are: (1) The chemical substance's
hazard and exposure potential; (2) the chemical substance's persistence
and bioaccumulation; (3) potentially exposed or susceptible
subpopulations; (4) storage of the chemical substance near significant
sources of drinking water; (5) the chemical substance's conditions of
use or significant changes in conditions of use; and (6) the chemical
substance's production volume or significant changes in production
volume. Because TSCA does not prohibit EPA from expanding the statutory
screening criteria, the proposed rule also provides an additional
criterion: (7) Any other risk-based criteria relevant to the
[[Page 4832]]
designation of the chemical substance's priority, in EPA's discretion.
This final criterion allows the screening review to adapt with future
changes in our understanding of science and chemical risks. In
addition, EPA fully recognizes the important role that stakeholders can
play in helping the Agency to identify candidates for prioritization or
to better understand the unique uses or characteristics of a particular
chemical. EPA continues to welcome this type of engagement and dialogue
early in the process, including during the pre-prioritization phase.
While the proposed rule provides multiple opportunities for public
feedback during the prioritization process, EPA is requesting comment
on whether and how EPA should solicit additional input at the pre-
prioritization phase.
The screening review is not a risk evaluation, but rather a review
of available information on the chemical substance that relates to the
screening criteria. EPA expects to evaluate all relevant sources of
information while conducting the screening review, including, as
appropriate, the hazard and exposure sources listed in Appendices A and
B of the 2012 TSCA Work Plan methodology (Ref. 4). Ultimately, the
screening review and other considerations during the pre-prioritization
phase are meant to inform EPA's decisions on (1) whether to initiate
the prioritization process on a particular chemical substance, and (2)
once initiated, the proposed designation of that chemical substance as
either a High-Priority Substances or Low-Priority Substance.
I. Initiation of Prioritization
The prioritization process officially begins, for purposes of
triggering the nine to twelve month statutory timeframe, when EPA
publishes a notice in the Federal Register identifying a chemical
substance for prioritization. The proposed rule also specifies that EPA
will publish the results of the screening review in the Federal
Register, describing the information, analysis and basis used to
conduct that review and providing in the docket copies of relevant
information not otherwise protected as confidential business
information under TSCA section 14. Publication of the notice in the
Federal Register also initiates a 90-day public comment period. For
each chemical substance, EPA will open a docket to facilitate receipt
of public comments and access to publicly available information
throughout this process. Interested persons can submit information
regarding the results of the screening review or any other information
relevant to the chemical substance. Of particular interest to EPA will
be information related to ``conditions of use'' that are missing from
the screening results. EPA will consider all relevant information
received during this comment period. Consistent with TSCA section
6(b)(1)(C)(iii), the proposed rule further allows EPA to extend this
initial public comment period for up to 3 months to receive and/or
evaluate information developed from a test order, commensurate with
EPA's need for additional time to receive and/or evaluate this
information. As a practical matter, EPA is unlikely to often extend
this initial public comment, given EPA's intention to ensure that all
or most of the necessary information is available before initiating the
prioritization process. Further, a three month window would not often
provide a sufficient time to gather, let alone consider, new test data
for the prioritization process. This is generally expected to be the
case even with the authority to more quickly collect such information
under the new test order authority in TSCA section 4.
J. Proposed Priority Designation
Based on the results of the screening review, relevant information
received from the public in the initial comment period, and other
information as appropriate, EPA will propose to designate the chemical
substance as either a High-Priority Substance or Low-Priority
Substance, as those terms are defined in TSCA. In making this proposed
designation, as directed by the statute, EPA will not consider costs or
other non-risk factors.
This proposed rule provides that EPA will publish the proposed
designation in the Federal Register, along with an identification of
the information, analysis and basis used to support a proposed
designation, in a form and manner that EPA deems appropriate, and
provide a second comment period of 90 days, during which time the
public may submit comments on EPA's proposed designation. EPA proposes
to use the same docket for this step of the process. Because the
supporting documentation for a proposed High-Priority Substance
designation is likely to foreshadow what will go into a scoping
document for risk evaluation, EPA will be particularly interested in
early comments on the accuracy of scope-related information such as the
chemical's ``conditions of use.''
In the event of insufficient information at the proposed
designation step, EPA is proposing to designate a chemical substance as
a High-Priority Substance. EPA expects this situation to occur
infrequently based on its application of the criteria and
considerations during the pre-prioritization phase. However, if for
some reason the information available to EPA is insufficient to support
a proposed designation of the chemical substance as a Low-Priority
Substance, including after any extension of the initial public comment
period, consistent with the statute, the proposed rule requires EPA to
propose to designate the chemical substance as a High-Priority
Substance. The statute requires that the prioritization process lead to
one of two outcomes by the end of the 12-month deadline: A High-
Priority Substance designation or a Low-Priority Substance designation.
15 U.S.C. 2605(b)(1)(B). There is no third option to allow EPA to
either require the development of additional information or otherwise
toll this deadline. Further, the statute specifically requires that a
Low-Priority Substance designation be based on ``information sufficient
to establish'' that a chemical substance meets the definition. 15
U.S.C. 2605(b)(1)(B)(ii). There is no comparable statutory requirement
for High-Priority Substance designations. 15 U.S.C. 2605(b)(1)(B)(i).
It is also relevant that the effect of designating a chemical as High-
Priority Substance is that EPA further evaluates the chemical
substance; by contrast, a Low-Priority Substance designation is a final
Agency determination that no further evaluation is warranted--a
determination that constitutes final agency action, subject to judicial
review. 15 U.S.C. 2618(a)(1)(C)(i).
The logical implication of this statutory structure is that
scientific uncertainty in this process (including as a result of
insufficient information) is to weigh in favor of a High-Priority
Substance designation, as it is merely an interim step that ensures
that the chemical will be further evaluated. EPA's proposal would also
ensure that this process would not create any incentives for parties to
withhold readily available information, or inadvertently discourage the
voluntary generation of data, as could occur were EPA to establish, for
example, a default designation to Low-Priority. As a practical matter,
however, EPA expects this situation to occur infrequently, based on its
proposed criteria and considerations that will generally ensure that
sufficient information is available to conduct a risk evaluation before
initiating prioritization. Priority designations, whether they were
based on sufficient information or a lack of sufficient information,
are neither an
[[Page 4833]]
affirmation of risk nor safety. EPA therefore recognizes that all
priority designations will need to be carefully communicated to the
public.
For proposed designations as Low-Priority Substances, EPA is
proposing to require that all comments that could be raised on the
issues in the proposed designation must be presented during the comment
period. Any issues not raised will be considered to have been waived,
and may not form the basis for an objection or challenge in any
subsequent administrative or judicial proceeding. This is a well-
established principle of administrative law and practice, e.g., Nuclear
Energy Institute v. EPA, 373 F.3d 1251, 1290-1291 (D.C. Cir. 2004), and
the need for such a provision is reinforced by the statutory deadlines
under which EPA must operate here. EPA is restricting this to Low-
Priority Substance designations, as it is the last opportunity for
public input before EPA's action becomes final, and thus it is
imperative that any issues are shared during this public comment
period. By contrast, designation of a chemical substance as a High-
Priority Substance is not final agency action. The statute mandates
additional opportunities for public input during the risk evaluation
process, and EPA does not consider it appropriate to restrict the
public's ability to comment during these subsequent processes based on
this early phase proceeding.
K. Final Priority Designation
After considering any additional information collected during the
proposed designation step, as appropriate, the last step in the
prioritization process is for EPA to finalize its designation of a
chemical substance as either a High-Priority Substance or a Low-
Priority Substance. The proposed rule specifies that EPA will publish
the priority designation in the Federal Register, and will use the same
docket. Again, TSCA prohibits costs or other non-risk factors from
being considered in this designation. And, as with the proposed
designation step, if information available to EPA remains insufficient
to support the final designation of the chemical substance as a Low-
Priority Substance, EPA will finalize the designation as a High-
Priority Substance. Although final High-Priority designations based on
insufficient information are unlikely for all the reasons described in
Unit III.J., such a designation would require EPA to conduct a risk
evaluation on that substance, and to support the risk evaluation with
adequate information. EPA would need to develop or require development
of the necessary information and complete the risk evaluation within
the 3-year statutory deadline.
L. Repopulation of High-Priority Substances
TSCA requires EPA to finalize a designation for at least one new
High-Priority Substance upon completion of a risk evaluation for
another chemical substance, other than a risk evaluation that was
requested by a manufacturer. Because the timing for the completion of
risk evaluation and/or the prioritization process will be difficult to
predict, EPA intends to satisfy this 1-off-1-on replacement obligation
as follows: In the notice published in the Federal Register finalizing
the designation of a new High-Priority Substance, EPA will identify the
complete or near-complete risk evaluation that the new High-Priority
Substance will replace. So long as the designation occurs within a
reasonable time before or after the completion of the risk evaluation,
this will satisfy Congress' intent while avoiding unnecessary delay and
the logistical challenges that would be associated with more perfectly
aligning a High-Priority Substance designation with the completion of a
risk evaluation.
M. Effect of Final Priority Designation
Final designation of a chemical substance as a High-Priority
Substance requires EPA to immediately begin a risk evaluation on that
chemical substance. It is important to note that High-Priority
Substance designation does not mean that the Agency has determined that
the chemical substance presents a risk to human health or the
environment--only that the Agency intends to consider the chemical
substance for further risk review and evaluation. A High-Priority
Substance designation is not a final agency action and is not subject
to judicial review or review under the Congressional Review Act (CRA),
5 U.S.C. 801 et seq.
Final designation of a chemical substance as a Low-Priority
Substance means that a risk evaluation of the chemical substance is not
warranted at the time, but does not preclude EPA from later revising
the designation, if warranted. Notably, a Low-Priority Substance
designation is explicitly subject to judicial review. 15 U.S.C.
2618(a)(1)(C).
N. Revision of Designation
TSCA provides that EPA may revise a final designation of a chemical
substance from a Low-Priority Substance to a High-Priority Substance at
any time based on information available to the Agency. The proposed
rule outlines the process the Agency will take to revise such a
designation. Specifically, EPA would (1) re-screen the chemical
substance incorporating the relevant information, (2) re-initiate the
prioritization process and take public comment, (3) re-propose a
priority designation and take public comment, and (4) re-finalize the
priority designation. EPA will not revise a final designation of a
chemical substance from High-Priority Substance to Low-Priority
Substance, but rather see the risk evaluation process through to its
conclusion.
IV. References
The following is a listing of the documents that are specifically
referenced in this document. The docket includes these documents and
other information considered by EPA, including documents that are
referenced within the documents that are included in the docket, even
if the referenced document is not physically located in the docket. For
assistance in locating these other documents, please consult the
technical person listed under FOR FURTHER INFORMATION CONTACT.
1. EPA. TSCA Work Plan for Chemical Assessments: 2014 Update.
October 2014. Available online at: https://www.epa.gov/sites/production/files/2015-01/documents/tsca_work_plan_chemicals_2014_update-final.pdf.
2. EPA. Framework for Metals Risk Assessment. EPA 120/R-07/001.
March 2007. Available online at: https://www.epa.gov/sites/production/files/2013-09/documents/metals-risk-assessment-final.pdf.
3. EPA. Science Policy Council Handbook: Risk Characterization. EPA/
100/B-00/002. December 2000. Available online at: https://www.epa.gov/risk/risk-characterization-handbook.
4. EPA. TSCA Work Plan Chemicals: Methods Document. February 2012.
Available online at: https://www.epa.gov/sites/production/files/2014-03/documents/work_plan_methods_document_web_final.pdf.
5. EPA. 2012 TSCA Work Plan Chemicals. June 2012. Available online
at: https://www.epa.gov/sites/production/files/2014-02/documents/work_plan_chemicals_web_final.pdf.
6. EPA. Safer Chemical Ingredients List (SCIL). Available online at:
https://www.epa.gov/saferchoice/safer-ingredients. See also Master
Criteria, September 2012, Version 2.1, available online at: https://www.epa.gov/sites/production/files/2013-12/documents/dfe_master_criteria_safer_ingredients_v2_1.pdf.
V. Statutory and Executive Order Reviews
Additional information about these statutes and Executive Orders
can be
[[Page 4834]]
found at https://www2.epa.gov/laws-regulations/laws-and-executive-orders.
A. Executive Order 12866: Regulatory Planning and Review and Executive
Order 13563: Improving Regulation and Regulatory Review
This action is a significant regulatory action that was submitted
to the Office of Management and Budget (OMB) for review under Executive
Orders 12866 (58 FR 51735, October 4, 1993) and 13563 (76 FR 3821,
January 21, 2011). Any changes made in response to OMB recommendations
have been documented in the docket.
B. Paperwork Reduction Act (PRA)
This action does not contain any information collection activities
that require approval under the PRA, 44 U.S.C. 3501 et seq. This
rulemaking addresses internal EPA operations and procedures and does
not impose any requirements on the public.
C. Regulatory Flexibility Act (RFA)
I certify under section 605(b) of the RFA, 5 U.S.C. 601 et seq.,
that this action will not have a significant economic impact on a
substantial number of small entities. This rulemaking addresses
internal EPA operations and procedures and does not impose any
requirements on the public, including small entities.
D. Unfunded Mandates Reform Act (UMRA)
This action does not contain any unfunded mandate as described in
UMRA, 2 U.S.C. 1531-1538, and does not significantly or uniquely affect
small governments. The action imposes no enforceable duty on any state,
local or tribal governments or the private sector.
E. Executive Order 13132: Federalism
This action does not have federalism implications as specified in
Executive Order 13132 (64 FR 43255, August 10, 1999). 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.
F. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
This action does not have tribal implications as specified in
Executive Order 13175 (65 FR 67249, November 9, 2000). It will not have
substantial direct effects on one or more Indian tribes, 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. Thus, Executive Order 13175 does not
apply to this action.
G. Executive Order 13045: Protection of Children From Environmental
Health Risks and Safety Risks
EPA interprets Executive Order 13045 (62 FR 19885, April 23, 1997)
as applying only to those regulatory actions that concern environmental
health or safety risks that the EPA has reason to believe may
disproportionately affect children, per the definition of ``covered
regulatory action'' in section 2-202 of the Executive Order. This
action is not subject to Executive Order 13045 because it does not
concern an environmental health risk or safety risk.
H. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
This action is not a ``significant energy action'' as defined in
Executive Order 13211 (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. This rulemaking addresses internal EPA operations and
procedures and does not impose any requirements on the public.
I. National Technology Transfer and Advancement Act (NTTAA)
This rulemaking does not involve any technical standards, and is
therefore not subject to considerations under NTTAA section 12(d), 15
U.S.C. 272 note.
J. Executive Order 12898: Federal Actions To Address Environmental
Justice in Minority Populations and Low-Income Populations
This action does not establish an environmental health or safety
standard, and is therefore not is not subject to environmental justice
considerations under Executive Order 12898 (59 FR 7629, February 16,
1994). This rulemaking addresses internal EPA operations and procedures
and does not have any impact on human health or the environment.
List of Subjects in 40 CFR Part 702
Environmental protection, Chemicals, Chemical substances, Hazardous
substances, Health and safety, Prioritization, Screening, Toxic
substances.
Dated: December 27, 2016
Gina McCarthy,
Administrator.
Therefore, 40 CFR chapter I, subchapter R, is proposed to be
amended as follows:
PART 702--[AMENDED]
0
1. The authority citation for part 702 is revised to read as follows:
Authority: 15 U.S.C. 2605 and 2619.
0
2. Add subpart A to read as follows:
PART 702--GENERAL PRACTICES AND PROCEDURES
Subpart A--Procedures for Prioritization of Chemical Substances for
Risk Evaluation
702.1 General Provisions.
702.3 Definitions.
702.5 Considerations for Potential Candidates for Prioritization.
702.7 Candidate Selection and Screening Review.
702.9 Initiation of Prioritization Process.
702.11 Proposed Priority Designation.
702.13 FinaL Priority Designation.
702.15 Revision of Designation.
702.17 Effect of Designation as a Low-Priority Substance.
702.19 Effect of Designation as a High-Priority Substance.
* * * * *
Authority: 15 U.S.C. 2605 and 2619.
Subpart A--Procedures for Prioritization of Chemical Substances for
Risk Evaluation
Sec. 702.1 General Provisions.
(a) Purpose. This regulation establishes the risk-based screening
process for designating chemical substances as a High-Priority
Substance or a Low-Priority Substance for risk evaluation as required
under section 6(b) of the Toxic Substances Control Act, as amended (15
U.S.C. 2605(b)).
(b) Scope of designations. EPA will make priority designations
pursuant to these procedures for a chemical substance, not for a
specific condition or conditions of use of a chemical substance.
(c) Categories of chemical substances. Nothing in this subpart
shall be interpreted as a limitation on EPA's authority under 15 U.S.C.
2625(c) to take action, including the actions contemplated in this
subpart, on a category of chemical substances.
(d) Prioritization timeframe. The Agency will publish a final
priority designation for a chemical substance in no fewer than 9 months
and no longer than 1 year following initiation of prioritization
pursuant to 40 CFR 702.9.
(e) Metals or metal compounds. In identifying priorities for
chemical
[[Page 4835]]
substances that are metals or metal compounds, EPA will, as
appropriate, refer to relevant considerations from the Framework for
Metals Assessment of the Office of the Science Advisor, Risk Assessment
Forum, dated March 2007, or a successor document that addresses metals
risk assessment and is peer reviewed by the Science Advisory Board.
(f) Applicability. These regulations do not apply to any chemical
substance for which a manufacturer requests a risk evaluation under
TSCA section 6(b)(4)(C) (15 U.S.C. 2605(b)(4)(C)).
Sec. 702.3 Definitions.
For purposes of this subpart, the following definitions apply:
Act means the Toxic Substances Control Act, as amended (15 U.S.C.
2601 et seq.)
EPA means the U.S. Environmental Protection Agency.
High-Priority Substance means a chemical substance that EPA
determines, without consideration of costs or other non-risk factors,
may present an unreasonable risk of injury to health or the environment
because of a potential hazard and a potential route of exposure under
the conditions of use, including an unreasonable risk to potentially
exposed or susceptible subpopulations identified as relevant by EPA.
Low-Priority Substance means a chemical substance that EPA
concludes, based on information sufficient to establish, without
consideration of costs or other non-risk factors, does not meet the
standard for a High-Priority Substance.
Sec. 702.5 Consideration of Potential Candidates for Prioritization.
(a) Potential High-Priority Substance Candidates. In identifying
potential candidates for High-Priority Substances, EPA will generally
consider whether information available to the Agency suggests there is
hazard and exposure under a condition or conditions of use, and whether
a risk evaluation would be needed to determine whether there is an
unreasonable risk of injury to health or the environment.
(b) Potential Low-Priority Substance Candidates. In identifying
potential candidates for Low-Priority Substances, EPA will generally
consider whether information available to the EPA suggests such low
hazard and/or exposure under all conditions of use that EPA is
confident the chemical substances does not present an unreasonable risk
of injury to health or the environment, including an unreasonable risk
to potentially exposed or susceptible subpopulations identified as
relevant by EPA, even in the absence of a risk evaluation.
(c) Exposure and Hazard Considerations for Potential Candidates.
In identifying potential candidates for prioritization, EPA will
generally evaluate whether or not the chemical substance meets one or
more of the following exposure or hazard considerations:
(1) Persistent, bioaccumulative, and toxic;
(2) Used in children's products;
(3) Used in consumer products;
(4) Detected in human and/or ecological biomonitoring programs;
(5) Potentially of concern for children's health;
(6) High acute and chronic toxicity;
(7) Probable or known carcinogen;
(8) Neurotoxicity; or
(9) Other emerging exposure and hazard concerns to human health or
the environment, as determined by the Agency.
A chemical substance that meets one or more of these criteria will
generally be considered as a potential candidate for further
consideration as a High-Priority Substance. A chemical substance that
meets none of these criteria will generally be considered as a
potential candidate for further consideration as a Low-Priority
Substance.
(d) Available Information and Resources. EPA expects it will often
be difficult to timely require development of necessary chemical
information, and receive, evaluate, and incorporate that information
into analyses, during the prioritization and risk evaluation processes,
within the statutory deadlines under the Act for prioritization and
risk evaluation at 15 U.S.C. 2605 (b)(1)(C) and (b)(4)(G). Therefore,
EPA will generally review and analyze the information necessary for
both prioritization and risk evaluation prior to initiating the
prioritization process for a chemical substance pursuant to 40 CFR
702.9. Specifically, in identifying potential candidates for
prioritization, EPA expects to consider:
(1) The availability of information and resources necessary and
sufficient to support a priority designation pursuant to 40 CFR 702.11,
a risk evaluation pursuant to 40 CFR 702, subpart B, or other such
action as determined by the Administrator; and
(2) The ability of EPA to timely develop or require development of
information necessary and sufficient to support a priority designation
pursuant to 40 CFR 702.11; a risk evaluation pursuant to 40 CFR 702,
subpart B; or other such action as determined by the Agency.
(e) Insufficient Information. In the absence of sufficient
information to support a priority designation pursuant to 40 CFR
702.11, a risk evaluation pursuant to 40 CFR 702, subpart B, or other
such action as determined by the Agency, EPA may use its authorities
under the Act, and other information gathering authorities, to gather
or require the generation of the needed information on a chemical
substance before initiating the prioritization process for that
chemical substance.
Sec. 702.7 Candidate Selection and Screening Review.
(a) Preferences and TSCA Work Plan. In selecting a candidate for
prioritization as a High-Priority Substance, EPA will:
(1) Give preference to:
(A) Chemical substances that are listed in the 2014 update of the
TSCA Work Plan for Chemical Assessments as having a persistence and
bioaccumulation score of 3, and
(B) Chemical substances that are listed in the 2014 update of the
TSCA Work Plan for Chemical Assessments that are known human
carcinogens and have high acute and chronic toxicity; and
(2) Identify a sufficient number of candidates from the 2014 update
of the TSCA Work Plan for Chemical Assessments to ensure that, at any
given time, at least 50 percent of risk evaluations being conducted by
EPA are drawn from that list until all substances on the list have been
designated as either a High-Priority Substance or Low-Priority
Substance pursuant to 40 CFR 702.13.
(b) General Objective. In selecting candidates for a High-Priority
Substance designation, it is EPA's general objective to select those
chemical substances with the greatest hazard and exposure potential
first, considering available information on the relative hazard and
exposure of potential candidates. EPA may also consider the relative
hazard and exposure of a potential candidate's substitutes. EPA is not
required to select candidates or initiate prioritization pursuant to 40
CFR 702.9 in any ranked or hierarchical order.
(c) Screening Review. Following selection of a candidate chemical
substance, EPA will generally use available information to screen the
candidate chemical substance against the following criteria and
considerations:
(1) The chemical substance's hazard and exposure potential;
[[Page 4836]]
(2) The chemical substance's persistence and bioaccumulation;
(3) Potentially exposed or susceptible subpopulations;
(4) Storage of the chemical substance near significant sources of
drinking water;
(5) The chemical substance's conditions of use or significant
changes in conditions of use;
(6) The chemical substance's production volume or significant
changes in production volume; and
(7) Any other risk-based criteria relevant to the designation of
the chemical substance's priority, in EPA's discretion.
(d) Information sources. In conducting the screening review in
paragraph (c) of this section, EPA expects to consider sources of
information relevant to the listed criteria, including, as appropriate,
sources for hazard and exposure data listed in Appendices A and B of
the TSCA Work Plan Chemicals: Methods Document (February 2012).
(e) The purpose of the preferences and criteria in paragraph (a) of
this section and the screening review in paragraph (c) of this section
are to inform EPA's decision whether or not to initiate the
prioritization process pursuant to 40 CFR 702.9, and the proposed
designation of the chemical substance as either a High-Priority
Substance or a Low-Priority Substance pursuant to 40 CFR 702.11.
(f) If, after the screening review in paragraph (c) of this
section, EPA believes it will not have sufficient information to
support a proposed priority designation pursuant to 40 CFR 702.11, a
risk evaluation pursuant to 40 CFR 702, subpart B, or other such action
as determined by the Agency, EPA is likely to use its authorities under
the Act, and other information gathering authorities, to generate the
needed information before initiating prioritization pursuant to 40 CFR
702.9.
Sec. 702.9 Initiation of Prioritization Process.
(a) EPA generally expects to initiate the prioritization process
for a chemical substance only when it believes that all or most of the
information necessary to prioritize and perform a risk evaluation on
the substance already exists.
(b) EPA will initiate prioritization by publishing a notice in the
Federal Register identifying a chemical substance for prioritization
and the results of the screening review conducted pursuant to 40 CFR
702.7(c).
(c) The prioritization timeframe in 40 CFR 702.1(d) begins upon
EPA's publication of the notice described in paragraph (b) of this
section.
(d) The results of the screening review published pursuant to
paragraph (b) of this section will identify, in a form and manner that
EPA deems appropriate, the information analysis and basis used in
conducting the screening process. Subject to 15 U.S.C. 2613, copies of
the information will also be placed in a public docket established for
each chemical substance.
(e) Publication of a notice in the Federal Register pursuant to
paragraph (b) of this section will initiate a period of 90 days during
which interested persons may submit relevant information on that
chemical substance. Relevant information might include, but is not
limited to, any information regarding the results of the screening
review conducted pursuant to 40 CFR 702.7(c), and any additional
information on the chemical substance that pertains to the criteria and
considerations at 40 CFR 702.7(c).
(f) EPA may, in its discretion, extend the public comment period in
paragraph (b) of this section for up to three months in order to
receive or evaluate information submitted under 15 U.S.C.
2603(a)(2)(B). The length of the extension will be based upon EPA's
assessment of the time necessary for EPA to receive and/or evaluate
information submitted under 15 U.S.C. 2603(a)(2)(B).
Sec. 702.11 Proposed Priority Designation.
(a) Based on the results of the screening review in 40 CFR
702.7(c), relevant information received from the public as described in
40 CFR 702.9(e), and other information as appropriate and in EPA's
discretion, EPA will propose to designate the chemical substance as
either a High-Priority Substance or Low-Priority Substance.
(b) EPA will not consider costs or other non-risk factors in making
a proposed priority designation.
(c) If information available to EPA remains insufficient to enable
the proposed designation of the chemical substance as a Low-Priority
Substance, including after any extension of the initial public comment
period pursuant to 40 CFR 702.9(f), EPA will propose to designate the
chemical substance as a High-Priority Substance.
(d) EPA may propose to designate a chemical substance as a High-
Priority Substance based on the proposed conclusion that the chemical
substance satisfies the definition of High-Priority Substance in 40 CFR
702.3 under any one or more uses that the Agency determines constitute
conditions of use as defined in 15 U.S.C. 2602. EPA will propose to
designate a chemical substance as a Low-Priority Substance based only
on the proposed conclusion that the chemical substance satisfies the
definition of Low-Priority Substance in 40 CFR 702.3 under all uses
that the Agency determines constitute conditions of use as defined in
15 U.S.C. 2602.
(e) EPA will publish the proposed designation in the Federal
Register, along with an identification of the information, analysis and
basis used to support a proposed designation, in a form and manner that
EPA deems appropriate, and provide a comment period of 90 days, during
which time the public may submit comment on EPA's proposed designation.
EPA will open a docket to facilitate receipt of public comment.
(f) For chemical substances that EPA proposes to designate as Low-
Priority Substances, EPA will specify in the notice published pursuant
to paragraph (e) of this section that all comments that could be raised
on the issues in the proposed designation must be presented during this
comment period. Any issues not raised at this time will be considered
to have been waived, and may not form the basis for an objection or
challenge in any subsequent administrative or judicial proceeding.
Sec. 702.13 Final Priority Designation.
(a) After considering any additional information collected from the
proposed designation process in 40 CFR 702.11, as appropriate, EPA will
finalize its designation of a chemical substance as either a High-
Priority Substance or a Low-Priority Substance.
(b) EPA will not consider costs or other non-risk factors in making
a final priority designation.
(c) EPA will publish each final priority designation in the Federal
Register.
(d) EPA will finalize a designation for at least one High-Priority
Substance for each risk evaluation it completes, other than a risk
evaluation that was requested by a manufacturer pursuant to 40 CFR 702,
subpart B. The obligation in 15 U.S.C. 2605(b)(3)(C) will be satisfied
by the designation of at least one High-Priority Substance where such
designation specifies the risk evaluation that the designation
corresponds to, and where the designation occurs within a reasonable
time before or after the completion of the risk evaluation.
(e) If information available to EPA remains insufficient to enable
the final designation of the chemical substance as a Low-Priority
Substance, EPA will finalize the designation of the chemical substance
as a High-Priority Substance.
[[Page 4837]]
Sec. 702.15 Revision of Designation.
EPA may revise a final designation of chemical substance from Low-
Priority to High-Priority Substance at any time based on information
available to the Agency. To revise such a designation, EPA will re-
screen the chemical substance pursuant to 40 CFR 702.7(c), re-initiate
the prioritization process on that chemical substance in accordance
with 40 CFR 702.9, propose a priority designation pursuant to 40 CFR
702.11, and finalize the priority designation pursuant to 40 CFR
702.13. EPA will not revise a final designation of a chemical substance
from a High-Priority Substance designation to Low-Priority.
Sec. 702.17 Effect of Designation as a Low-Priority Substance.
Designation of a chemical substance as a Low-Priority Substance
under 40 CFR 702.3 means that a risk evaluation of the chemical
substance is not warranted at the time, but does not preclude EPA from
later revising the designation pursuant to 40 CFR 702.15, if warranted.
Sec. 702.19 Effect of Designation as a High-Priority Substance.
Final designation of a chemical substance as a High-Priority
Substance under 40 CFR 702.13 initiates a risk evaluation pursuant to
40 CFR 702, subpart B. Designation as a High-Priority Substance is not
a final agency action and is not subject to judicial review.
* * * * *
[FR Doc. 2017-00051 Filed 1-13-17; 8:45 am]
BILLING CODE 6560-50-P