Protection of Stratospheric Ozone: The 2013 Critical Use Exemption From the Phaseout of Methyl Bromide, 74435-74449 [2012-30225]
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Federal Register / Vol. 77, No. 241 / Friday, December 14, 2012 / Proposed Rules
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 82
[EPA–HQ–OAR–2010–0280; FRL–9714–4]
RIN 2060–AR41
Protection of Stratospheric Ozone: The
2013 Critical Use Exemption From the
Phaseout of Methyl Bromide
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
SUMMARY: EPA is proposing uses that
qualify for the 2013 critical use
exemption. EPA is also proposing to
amend the regulatory framework to
determine the amount of methyl
bromide that may be produced,
imported, or supplied from existing prephaseout inventory for those uses in
2013. EPA is taking action under the
authority of the Clean Air Act to reflect
a recent consensus decision taken by the
Parties to the Montreal Protocol on
Substances that Deplete the Ozone
Layer at the Twenty-Third Meeting of
the Parties. EPA is seeking comment on
the list of critical uses and on EPA’s
determination of the specific amounts of
methyl bromide that may be produced
and imported, or sold from pre-phaseout
inventory for those uses.
DATES: Comments must be submitted by
January 28, 2013. Any party requesting
a public hearing must notify the contact
person listed below by 5 p.m. Eastern
Standard Time on December 19, 2012. If
a hearing is requested it will be held on
December 31, 2012. EPA will post
information regarding a hearing, if one
is requested, on the Ozone Protection
Web site www.epa.gov/ozone/
strathome.html. Persons interested in
attending a public hearing should
consult with the contact person below
regarding the location and time of the
hearing.
Submit your comments,
identified by Docket ID No. EPA–HQ–
OAR–2010–0280, by one of the
following methods:
• www.regulations.gov: Follow the
on-line instructions for submitting
comments.
• Email: a-and-r-Docket@epa.gov.
• Fax: (202) 566–9744.
• Phone: (202) 566–1742.
• U.S. Mail: Docket EPA–HQ–OAR–
2010–0280, U.S. Environmental
Protection Agency, EPA Docket Center,
Air and Radiation Docket, Mail Code
28221T, 1200 Pennsylvania Avenue
NW., Washington, DC 20460.
• Hand Delivery or Courier: Docket
EPA–HQ–OAR–2010–0280, EPA Docket
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ADDRESSES:
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Center—Public Reading Room, EPA
West Building, Room 3334, 1301
Constitution Avenue NW., Washington,
DC 20004. Such deliveries are only
accepted during the Docket’s normal
hours of operation, and special
arrangements should be made for
deliveries of boxed information.
Instructions: Direct your comments to
Docket ID No. EPA–HQ–OAR–2010–
0280. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through www.regulations.gov
or email. The www.regulations.gov Web
site is an ‘‘anonymous access’’ system,
which means EPA will not know your
identity or contact information unless
you provide it in the body of your
comment. If you send an email
comment directly to EPA without going
through www.regulations.gov your email
address will be automatically captured
and included as part of the comment
that is placed in the public docket and
made available on the Internet. If you
submit an electronic comment, EPA
recommends that you include your
name and other contact information in
the body of your comment and with any
disk or CD–ROM you submit. If EPA
cannot read your comment due to
technical difficulties and cannot contact
you for clarification, EPA may not be
able to consider your comment.
Electronic files should avoid the use of
special characters, any form of
encryption, and be free of any defects or
viruses. For additional information
about EPA’s public docket visit the EPA
Docket Center homepage at https://
www.epa.gov/epahome/dockets.htm.
Docket: All documents in the docket
are listed in the www.regulations.gov
index. Although listed in the index,
some information is not publicly
available, e.g., CBI or other information
whose disclosure is restricted by statute.
Certain other material, such as
copyrighted material, will be publicly
available only in hard copy. Publicly
available docket materials are available
either electronically in
www.regulations.gov or in hard copy at
the Air and Radiation Docket, EPA/DC,
EPA West, Room 3334, 1301
Constitution Ave. NW., Washington,
DC. The Public Reading Room is open
from 8:30 a.m. to 4:30 p.m., Monday
through Friday, excluding legal
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holidays. The telephone number for the
Public Reading Room is (202) 566–1744,
and the telephone number for the Air
and Radiation Docket is (202) 566–
1742).
FOR FURTHER INFORMATION CONTACT: For
further information about this proposed
rule, contact Jeremy Arling by telephone
at (202) 343–9055, or by email at
arling.jeremy@epa.gov or by mail at U.S.
Environmental Protection Agency,
Stratospheric Protection Division,
Stratospheric Program Implementation
Branch (6205J), 1200 Pennsylvania
Avenue NW., Washington, DC 20460.
You may also visit the methyl bromide
section of the Ozone Depletion Web site
of EPA’s Stratospheric Protection
Division at www.epa.gov/ozone/mbr for
further information about the methyl
bromide critical use exemption, other
Stratospheric Ozone Protection
regulations, the science of ozone layer
depletion, and related topics.
SUPPLEMENTARY INFORMATION: This
proposed rule concerns Clean Air Act
(CAA) restrictions on the consumption,
production, and use of methyl bromide
(a Class I, Group VI controlled
substance) for critical uses during
calendar year 2013. Under the Clean Air
Act, methyl bromide consumption
(consumption is defined under section
601 of the CAA as production plus
imports minus exports) and production
were phased out on January 1, 2005,
apart from allowable exemptions, such
as the critical use and the quarantine
and preshipment (QPS) exemptions.
With this action, EPA is proposing and
seeking comment on the uses that will
qualify for the 2013 critical use
exemption as well as specific amounts
of methyl bromide that may be
produced and imported, or sold from
pre-phaseout inventory (also referred to
as ‘‘stocks’’ or ‘‘inventory’’) for proposed
critical uses in 2013.
Table of Contents
I. General Information
A. Regulated Entities
B. What should I consider when preparing
my comments?
II. What is methyl bromide?
III. What is the background to the phaseout
regulations for ozone-depleting
substances?
IV. What is the legal authority for exempting
the production and import of methyl
bromide for critical uses authorized by
the parties to the Montreal Protocol?
V. What is the critical use exemption
process?
A. Background of the Process
B. How does this proposed rule relate to
previous critical use exemption rules?
C. Stocks of Methyl Bromide
D. Proposed Critical Uses
E. Proposed Critical Use Amounts
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1. Approach for Determining Critical Stock
Allowances
2. Approach for Determining New
Production and Import Allowances
F. The Criteria in Decisions IX/6 and Ex.
I/4
G. Emissions Minimization
VI. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer and
Advancement Act
J. Executive Order 12898: Federal Actions
to Address Environmental Justice in
Minority Populations and Low-Income
Populations
I. General Information
A. Regulated Entities
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Entities potentially regulated by this
proposed action are those associated
with the production, import, export,
sale, application, and use of methyl
bromide covered by an approved critical
use exemption. Potentially regulated
categories and entities include
producers, importers, and exporters of
methyl bromide; applicators and
distributors of methyl bromide; and
users of methyl bromide that applied for
the 2013 critical use exemption
including growers of vegetable crops,
fruits and nursery stock, and owners of
stored food commodities and structures
such as grain mills and processors. This
list is not intended to be exhaustive, but
rather to provide a guide for readers
regarding entities likely to be regulated
by this proposed action. To determine
whether your facility, company,
business, or organization could be
regulated by this proposed action, you
should carefully examine the
regulations promulgated at 40 CFR part
82, subpart A. If you have questions
regarding the applicability of this action
to a particular entity, consult the person
listed in the preceding section.
B. What should I consider when
preparing my comments?
1. Confidential Business Information.
Do not submit confidential business
information (CBI) to EPA through
www.regulations.gov or email. Clearly
mark the part or all of the information
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that you claim to be CBI. For CBI
information in a disk or CD–ROM that
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. Information so
marked will not be disclosed except in
accordance with procedures set forth in
40 CFR part 2. 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.
2. Tips for Preparing Your Comments.
When submitting comments, remember
to:
• Identify the rulemaking by docket
number and other identifying
information (subject heading, Federal
Register date, and page number).
• Follow directions—The agency may
ask you to respond to specific questions
or organize comments by referencing a
Code of Federal Regulations (CFR) part
or section number.
• Explain why you agree or disagree;
suggest alternatives and substitute
language for your requested changes.
• Describe any assumptions and
provide any technical information and/
or data that you used.
• If you estimate potential costs or
burdens, explain how you arrived at
your estimate in sufficient detail to
allow for it to be reproduced.
• Provide specific examples to
illustrate your concerns, and suggest
alternatives.
• Explain your views as clearly as
possible, avoiding the use of profanity
or personal threats.
• Make sure to submit your
comments by the comment period
deadline identified.
II. What is methyl bromide?
Methyl bromide is an odorless,
colorless, toxic gas which is used as a
broad-spectrum pesticide and is
controlled under the CAA as a Class I
ozone-depleting substance (ODS).
Methyl bromide was once widely used
as a fumigant to control a variety of
pests such as insects, weeds, rodents,
pathogens, and nematodes. Information
on methyl bromide can be found at
https://www.epa.gov/ozone/mbr.
Methyl bromide is also regulated by
EPA under the Federal Insecticide,
Fungicide, and Rodenticide Act (FIFRA)
and other statutes and regulatory
authority, as well as by States under
their own statutes and regulatory
authority. Under FIFRA, methyl
bromide is a restricted use pesticide.
Restricted use pesticides are subject to
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Federal and State requirements
governing their sale, distribution, and
use. Nothing in this proposed rule
implementing the Clean Air Act is
intended to derogate from provisions in
any other Federal, State, or local laws or
regulations governing actions including,
but not limited to, the sale, distribution,
transfer, and use of methyl bromide.
Entities affected by this proposal must
continue to comply with FIFRA and
other pertinent statutory and regulatory
requirements for pesticides (including,
but not limited to, requirements
pertaining to restricted use pesticides)
when importing, exporting, acquiring,
selling, distributing, transferring, or
using methyl bromide for critical uses.
The provisions in this proposed action
are intended only to implement the
CAA restrictions on the production,
consumption, and use of methyl
bromide for critical uses exempted from
the phaseout of methyl bromide.
III. What is the background to the
phaseout regulations for ozonedepleting substances?
The regulatory requirements of the
stratospheric ozone protection program
that limit production and consumption
of ozone-depleting substances are in 40
CFR part 82, subpart A. The regulatory
program was originally published in the
Federal Register on August 12, 1988 (53
FR 30566), in response to the 1987
signing and subsequent ratification of
the Montreal Protocol on Substances
that Deplete the Ozone Layer (Montreal
Protocol). The Montreal Protocol is the
international agreement aimed at
reducing and eliminating the
production and consumption of
stratospheric ozone-depleting
substances. The United States was one
of the original signatories to the 1987
Montreal Protocol and the United States
ratified the Protocol on April 12, 1988.
Congress then enacted, and President
George H.W. Bush signed into law, the
Clean Air Act Amendments of 1990
(CAAA of 1990) which included Title VI
on Stratospheric Ozone Protection,
codified as 42 U.S.C. Chapter 85,
Subchapter VI, to ensure that the United
States could satisfy its obligations under
the Protocol. EPA issued regulations to
implement this legislation and has since
amended the regulations as needed.
Methyl bromide was added to the
Protocol as an ozone-depleting
substance in 1992 through the
Copenhagen Amendment to the
Protocol. The Parties to the Montreal
Protocol (Parties) agreed that each
developed country’s level of methyl
bromide production and consumption
in 1991 should be the baseline for
establishing a freeze on the level of
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methyl bromide production and
consumption for developed countries.
EPA published a final rule in the
Federal Register on December 10, 1993
(58 FR 65018), listing methyl bromide as
a Class I, Group VI controlled substance.
This rule froze U.S. production and
consumption at the 1991 baseline level
of 25,528,270 kilograms, and set forth
the percentage of baseline allowances
for methyl bromide granted to
companies in each control period (each
calendar year) until 2001, when the
complete phaseout would occur. This
phaseout date was established in
response to a petition filed in 1991
under sections 602(c)(3) and 606(b) of
the CAAA of 1990, requesting that EPA
list methyl bromide as a Class I
substance and phase out its production
and consumption. This date was
consistent with section 602(d) of the
CAAA of 1990, which, for newly listed
Class I ozone-depleting substances
provides that ‘‘no extension [of the
phaseout schedule in section 604] under
this subsection may extend the date for
termination of production of any class I
substance to a date more than 7 years
after January 1 of the year after the year
in which the substance is added to the
list of class I substances.’’
At the Seventh Meeting of the Parties
(MOP) in 1995, the Parties made
adjustments to the methyl bromide
control measures and agreed to
reduction steps and a 2010 phaseout
date for developed countries with
exemptions permitted for critical uses.
At that time, the United States
continued to have a 2001 phaseout date
in accordance with section 602(d) of the
CAAA of 1990. At the Ninth MOP in
1997, the Parties agreed to further
adjustments to the phaseout schedule
for methyl bromide in developed
countries, with reduction steps leading
to a 2005 phaseout. The Parties also
established a phaseout date of 2015 for
Article 5 countries.
IV. What is the legal authority for
exempting the production and import of
methyl bromide for critical uses
authorized by the parties to the
Montreal Protocol?
In October 1998, the U.S. Congress
amended the Clean Air Act (CAA) to
prohibit the termination of production
of methyl bromide prior to January 1,
2005, to require EPA to bring the U.S.
phaseout of methyl bromide in line with
the schedule specified under the
Protocol, and to authorize EPA to
provide certain exemptions. These
amendments were contained in Section
764 of the 1999 Omnibus Consolidated
and Emergency Supplemental
Appropriations Act (Pub. L. 105–277,
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October 21, 1998) and were codified in
section 604 of the CAA, 42 U.S.C.
7671c. The amendment that specifically
addresses the critical use exemption
appears at section 604(d)(6), 42 U.S.C.
7671c(d)(6). EPA revised the phaseout
schedule for methyl bromide production
and consumption in a direct final
rulemaking on November 28, 2000 (65
FR 70795), which allowed for the
reduction in methyl bromide
consumption specified under the
Protocol and extended the phaseout to
2005 while creating a placeholder for
critical use exemptions. EPA again
amended the regulations to allow for an
exemption for quarantine and
preshipment (QPS) purposes through an
interim final rule on July 19, 2001 (66
FR 37751), and a final rule on January
2, 2003 (68 FR 238).
On December 23, 2004 (69 FR 76982),
EPA published a final rule (the
‘‘Framework Rule’’) that established the
framework for the critical use
exemption, set forth a list of approved
critical uses for 2005, and specified the
amount of methyl bromide that could be
supplied in 2005 from stocks and new
production or import to meet the needs
of approved critical uses. EPA
subsequently published rules applying
the critical use exemption framework
for each of the annual control periods
from 2006 to 2012. Under authority of
section 604(d)(6) of the CAA, today’s
action proposes the uses that will
qualify as approved critical uses in 2013
and the amount of methyl bromide that
may be produced, imported, or supplied
from inventory to satisfy those uses.
This proposed action on critical uses
for 2013 reflects Decision XXIII/4, taken
at the Twenty-Third Meeting of the
Parties in November 2011. In
accordance with Article 2H(5), the
Parties have issued several Decisions
pertaining to the critical use exemption.
These include Decisions IX/6 and Ex. I/
4, which set forth criteria for reviewing
proposed critical uses. The status of
Decisions is addressed in NRDC v. EPA,
(464 F.3d 1, DC Cir. 2006) and in EPA’s
‘‘Supplemental Brief for the
Respondent,’’ filed in NRDC v. EPA and
available in the docket for this action. In
this proposed rule on critical uses for
2013, EPA is honoring commitments
made by the United States in the
Montreal Protocol context.
V. What is the critical use exemption
process?
A. Background of the Process
The critical use exemption is
designed to permit the production and
import of methyl bromide for uses that
do not have technically and
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economically feasible alternatives that
are acceptable from the standpoint of
environment and health and for which
the lack of methyl bromide would result
in significant market disruption (40 CFR
82.3). Article 2H of the Montreal
Protocol established the critical use
exemption provision. At the Ninth
Meeting of the Parties (1997), the Parties
established the criteria for an exemption
in Decision IX/6. In that Decision, the
Parties agreed that ‘‘a use of methyl
bromide should qualify as ‘critical’ only
if the nominating Party determines that:
(i) The specific use is critical because
the lack of availability of methyl
bromide for that use would result in a
significant market disruption; and (ii)
there are no technically and
economically feasible alternatives or
substitutes available to the user that are
acceptable from the standpoint of
environment and public health and are
suitable to the crops and circumstances
of the nomination.’’ These criteria are
reflected in EPA’s definition of ‘‘critical
use’’ at 40 CFR 82.3. In addition, the
Parties decided that production and
consumption, if any, of methyl bromide
for critical uses should be permitted
only if a variety of conditions have been
met, including that all technically and
economically feasible steps have been
taken to minimize the critical use and
any associated emission of methyl
bromide, that research programs are in
place to develop and deploy alternatives
and substitutes, and that methyl
bromide is not available in sufficient
quantity and quality from existing
stocks of banked or recycled methyl
bromide.
In response to EPA’s request for
critical use exemption applications
published in the Federal Register on
July 15, 2010 (75 FR 41177), applicants
provided data on the technical and
economic feasibility of using
alternatives to methyl bromide.
Applicants also submitted data on their
use of methyl bromide, ongoing research
programs into the use of alternatives to
methyl bromide in their sector, and
efforts to minimize use and emissions of
methyl bromide.
EPA reviews the data submitted by
applicants, as well as data from
governmental and academic sources, to
establish whether there are technically
and economically feasible alternatives
available for a particular use of methyl
bromide, and whether there would be a
significant market disruption if no
exemption were available. In addition,
an interagency workgroup reviews other
parameters of the exemption
applications such as dosage and
emissions minimization techniques and
applicants’ research or transition plans.
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This assessment process culminates in
the development of a document referred
to as the U.S. critical use nomination
(CUN). Since 2003, the U.S. Department
of State has submitted a CUN annually
to the United Nations Environment
Programme (UNEP) Ozone Secretariat.
The Methyl Bromide Technical Options
Committee (MBTOC) and the
Technology and Economic Assessment
Panel (TEAP), which are advisory
bodies to Parties to the Montreal
Protocol, review each Party’s CUN and
make recommendations to the Parties on
the nominations. The Parties then take
Decisions to authorize critical use
exemptions for particular Parties,
including how much methyl bromide
may be supplied for the exempted
critical uses. As required in section
604(d)(6) of the CAA, for each
exemption period, EPA consults with
the United States Department of
Agriculture (USDA) and other
departments and institutions of the
Federal government that have regulatory
authority related to methyl bromide,
and provides an opportunity for public
comment on the amounts and specific
uses of methyl bromide that the agency
is proposing to exempt.
On February 4, 2011, the U.S.
Government (USG) submitted the ninth
Nomination for a Critical Use
Exemption for Methyl Bromide for the
United States of America to the Ozone
Secretariat of UNEP. This nomination
contained the request for 2013 critical
uses. In February 2011, MBTOC sent
questions to the USG concerning
technical and economic issues in the
2013 nomination. The USG transmitted
responses to MBTOC in February, 2011.
These documents, together with reports
by the advisory bodies noted above, are
in the public docket for this rulemaking.
The proposed critical uses and amounts
reflect the analysis contained in those
documents.
B. How does this proposed rule relate to
previous critical use exemption rules?
The December 23, 2004, Framework
Rule (69 FR 76982) established the
framework for the critical use
exemption program in the United States,
including definitions, prohibitions,
trading provisions, and recordkeeping
and reporting obligations. The preamble
to the Framework Rule included EPA’s
determinations on key issues for the
critical use exemption program.
Since publishing the Framework Rule,
EPA has annually promulgated
regulations to exempt specific quantities
of production and import of methyl
bromide, to determine the amounts that
may be supplied from pre-phaseout
inventory, and to indicate which uses
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meet the criteria for the exemption
program for that year. See 71 FR 5985
(February 6, 2006), 71 FR 75386
(December 14, 2006), 72 FR 74118
(December 28, 2007), 74 FR 19878
(April 30, 2009), 75 FR 23167 (May 3,
2010), 76 FR 60737 (September 30,
2011), and 77 FR 29218 (May 17, 2012).
Today’s action proposes to amend the
regulatory framework to determine the
amounts of Critical Use Allowances
(CUAs) and Critical Stock Allowances
(CSAs) to be allocated for critical uses
in 2013. A CUA is the privilege granted
through 40 CFR part 82 to produce or
import 1 kg of methyl bromide for an
approved critical use during the
specified control period. These
allowances expire at the end of the
control period and, as explained in the
Framework Rule, are not bankable from
one year to the next. The proposed CUA
allocation is subject to the trading
provisions at 40 CFR 82.12, which are
discussed in section V.G. of the
preamble to the Framework Rule (69 FR
76982).
A CSA is the right granted through 40
CFR part 82 to sell 1 kg of methyl
bromide from inventory produced or
imported prior to the January 1, 2005,
phaseout date for an approved critical
use during the specified control period.
The Framework Rule established
provisions governing the sale of prephaseout inventories for critical uses,
including the concept of CSAs and a
prohibition on the sale of pre-phaseout
inventories for critical uses in excess of
the amount of CSAs held by the seller.
It also established trading provisions
that allow CUAs to be converted into
CSAs.
C. Stocks of Methyl Bromide
An approved critical user may
purchase methyl bromide produced or
imported with CUAs, as well as limited
inventories of pre-phaseout methyl
bromide, the combination of which
constitute the supply of ‘‘critical use
methyl bromide’’ intended to meet the
needs of approved critical uses. EPA
considers all pre-phaseout inventory to
be suitable for both pre-plant and post
harvest uses. The aggregate amount of
pre-phaseout methyl bromide reported
as being in inventory at the beginning of
2012 is 1,248,876 kg. This amount does
not include critical use methyl bromide
that was produced after January 1, 2005,
and carried over into subsequent years.
Nor does it include methyl bromide
produced (1) Under the quarantine and
preshipment (QPS) exemption, (2) with
Article 5 allowances to meet the basic
domestic needs of Article 5 countries, or
(3) for feedstock or transformation
purposes. As in prior years, the Agency
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will continue to closely monitor CUA
and CSA data. As stated in the final
2006 CUE Rule, if an inventory shortage
occurs, EPA may consider various
options including authorizing the
conversion of a limited number of CSAs
to CUAs through a rulemaking, bearing
in mind the upper limit on U.S.
production/import for critical uses. In
sections V.D. and V.G. of this preamble,
EPA seeks comment on the amount of
critical use methyl bromide to come
from inventory compared to new
production and import.
As explained in the 2008 CUE Rule,
the agency intends to continue releasing
aggregate methyl bromide inventory
information reported to the agency
under the reporting requirements at 40
CFR 82.13 at the end of each control
period. EPA notes that if the number of
competitors in the industry were to
decline appreciably, EPA would revisit
the question of whether the aggregate is
entitled to treatment as confidential
information and whether to release the
aggregate without notice. EPA is not
proposing to change the treatment of
submitted information but welcomes
information concerning the composition
of the industry in this regard. The
aggregate information for 2003 through
2012 is available in the docket for this
rulemaking.
D. Proposed Critical Uses
In Decision XXIII/4, taken in
November 2011, the Parties to the
Protocol agreed ‘‘to permit, for the
agreed critical-use categories for 2013
set forth in table A of the annex to the
present decision for each party, subject
to the conditions set forth in the present
decision and in decision Ex.I/4 to the
extent that those conditions are
applicable, the levels of production and
consumption for 2013 set forth in table
B of the annex to the present decision
which are necessary to satisfy critical
uses * * * ’’
The following uses are those set forth
in table A of the annex to Decision
XXIII/4 for the United States:
•
•
•
•
•
•
•
•
•
•
•
•
Commodities
Mills and food processing structures
Dried cured pork
Cucurbits
Eggplant—field
Nursery stock—fruit, nuts, flowers
Orchard replants
Ornamentals
Peppers—field
Strawberry—field
Strawberry runners
Tomatoes—field
EPA is seeking comment on the
technical analysis contained in the U.S.
nomination (available for public review
in the docket to this rulemaking), and
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seeks information regarding any changes
to the registration (including
cancellation or new registrations), use,
or efficacy of alternatives that have
transpired after the 2013 U.S. CUN was
forwarded. EPA recognizes that as the
market for alternatives evolves, the
thresholds for what constitutes
‘‘significant market disruption’’ or
‘‘technical and economic feasibility’’
may change. Comments on technical
data contained in the CUN, or new
information, could potentially alter the
agency’s analysis on the uses and
amounts of methyl bromide qualifying
for the critical use exemption. The
agency may, in response to new
information, reduce the proposed
quantities of critical use methyl
bromide, or decide not to approve uses
authorized by the Parties. However, the
agency will not increase the quantities
or add new uses in the final rule beyond
those authorized by the Parties.
EPA is also proposing to modify the
table in 40 CFR part 82, subpart A,
appendix L to reflect the agreed critical
use categories identified in Decision
XXIII/4. The agency is amending the
table of critical uses and critical users
based in part on the technical analysis
contained in the 2013 U.S. nomination
that assesses data submitted by
applicants to the CUE program. First,
EPA is proposing to remove two users
who did not submit applications and
therefore were not included in the U.S.
nomination. These users are California
rose nursery growers and Maryland
tomato growers.
Second, EPA is proposing to remove
the National Pest Management
Association (NPMA) food processing
use from the list for 2013. The NPMA
did not initially apply to be a critical
user in 2013 and the Parties have not
authorized a critical use for this purpose
for 2013. Members of the NPMA have
worked to transition from methyl
bromide to alternative practices and
alternative fumigants like sulfuryl
fluoride. In January 2004, EPA
registered the first food uses of sulfuryl
fluoride for control of insect pests in
grain processing facilities and in
harvested and processed food
commodities such as cereal grains, dried
fruits, and tree nuts. In July 2005, EPA
approved sulfuryl fluoride for treatment
of additional harvested and processed
food commodities such as coffee and
cocoa beans, and for fumigation of food
handling and processing facilities.
On January 19, 2011, EPA proposed to
revoke the residue limits on food,
known as tolerances, for fluoride on the
food commodities approved for
treatment with sulfuryl fluoride (76 FR
3422). In response to this proposal, the
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NPMA submitted a supplemental
request for 2013 during the open period
for 2014 applications. The USG did not
include NPMA’s supplemental request
in the 2014 nomination submitted to
UNEP on January 31, 2012, because EPA
has only proposed to revoke the
tolerances for sulfuryl fluoride and has
not taken action in any final rule. U.S.
critical use nominations have been
based on final decisions about
alternatives. Additionally, the proposed
tolerance revocation rule includes a
staggered implementation scheme,
making it unlikely that any specific
revocation will be effective in 2013.
Therefore, EPA is not proposing NPMA
as a critical use in 2013.
Third, EPA is proposing to remove
sectors or users that applied for a
critical use in 2013 but that the United
States did not nominate for 2013. EPA
conducted a thorough technical
assessment of each application and
considered the effects that the loss of
methyl bromide would have for each
agricultural sector, and whether
significant market disruption would
occur as a result. As a result of this
technical review, the U.S. Government
did not find that certain sectors or users
met the critical use criteria in Decision
IX/6 and they were therefore not
included in the 2013 Critical Use
Nomination. EPA notified these sectors
of their status in July 2011. These
sectors are: members of the
Southeastern Cucurbit Consortium and
cucurbit growers in Maryland and
Delaware; growers in the forest nursery
sector (Southern Forest Nursery
Management Cooperative, Northeastern
Forest and Conservation Nursery
Association, and Michigan seedling
growers); members of the Southeastern
Pepper Consortium; members of the
Southeastern Strawberry Consortium
and Florida strawberry growers;
California sweet potato slip growers;
members of the Southeastern Tomato
Consortium and Virginia tomato
growers. For each of these uses, EPA
found that there are technically and
economically feasible alternatives to
methyl bromide.
Finally, EPA is proposing to limit the
CUE for cucurbit, eggplant, pepper, and
tomato sectors in Georgia to small
growers. The EPA review of the
available information for Georgia
indicates that farmers growing fewer
than 10 acres of these crops need an
additional year to successfully
transition to the alternatives. These
small growers do not have as much
experience with the alternatives and
need to convert their equipment to the
University of Georgia (UGA) ‘‘3-Way’’
mixture (a combination of 1,3-
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dichloropropene, chloropicrin, and
metam). The EPA conducted an
economic assessment of small growers’
ability to convert their equipment (see
revised nomination, dated July 15, in
the docket). The assessment
demonstrates that despite the UGA 3Way mixture being more affordable than
methyl bromide plus chloropicrin on a
per acre basis, retrofitting farm
equipment to use the UGA 3-Way
mixture at a cost of $3,450 is not
affordable for growers under four acres,
amortized over 10 years at 7% interest
(7% is a home equity loan rate for this
region at the time the nomination was
submitted; interest on agricultural loans
could be lower). However, due to
variations in impacts for individual
growers and uncertainties in the
assumptions used in the economic
analysis, farms smaller than 10 acres are
reasonably expected to incur negative
impacts from having to covert to the
UGA 3-Way mixture. Therefore, EPA is
proposing to limit the Georgia cucurbit,
eggplant, pepper, and tomato critical
uses to small growers, which EPA is
proposing to define as growers growing
fewer than 10 acres. EPA seeks
comment on these proposed changes to
Appendix L.
EPA is not proposing other changes to
the table but is repeating the following
clarifications made in previous years for
ease of reference. The ‘‘local township
limits prohibiting 1,3-dichloropropene’’
are prohibitions on the use of 1,3dichloropropene products in cases
where local township limits on use of
this alternative have been reached. In
addition, ‘‘pet food’’ under subsection B
of Food Processing refers to food for
domesticated dogs and cats. Finally,
‘‘rapid fumigation’’ for commodities is
when a buyer provides short (two
working days or fewer) notification for
a purchase or there is a short period
after harvest in which to fumigate and
there is limited silo availability for
using alternatives.
E. Proposed Critical Use Amounts
Table A of the annex to Decision
XXIII/4 lists critical uses and amounts
agreed to by the Parties to the Montreal
Protocol. When added together, the total
authorized critical use for 2013 for the
United States is 562,326 kilograms (kg),
which is equivalent to 2.2% of the U.S.
1991 methyl bromide consumption
baseline of 25,528,270 kg. The
maximum amount of new production
and import for U.S. critical uses,
specified in Table B of Decision XXIII/
4, is 562,326 kg, minus available stocks.
In previous years, the maximum amount
of new production has been less than
the total authorization, with the
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difference representing the minimum
amount that the Parties expect to be
used from pre-phaseout inventory. For
2013 the Parties indicated that the
United States should use ‘‘available
stocks,’’ but unlike previous years,
Decision XXIII/4 did not indicate a
minimum amount expected to be taken
from stocks. Consistent with EPA’s past
practice, and our commitments to the
Parties, EPA is considering the level of
‘‘available stocks’’ that may be allocated
in this rulemaking. However, EPA is
seeking comment on changing the
approach for determining the
availability of stocks in this rule.
As established in earlier rulemakings,
EPA views the determination of the total
allocation, up to the amount authorized
by the Parties, as an appropriate
exercise of discretion. The Agency may
decide to allocate less than the full
amount authorized by the Parties, and
in past CUE rules EPA has made
reductions to the total allocation after
considering several factors, including
new data on alternatives, such as the
registration of a new alternative not
considered when the CUN was
submitted to UNEP, and carryover from
prior years. For 2013, EPA does not
have new data regarding the uptake of
new alternatives. However,
iodomethane, an alternative that was
available when the CUN was submitted,
is no longer available. EPA believes this
is an important factor that should be
considered in determining the total
amount of the allocation; however,
because of the schedule for
consideration under the Montreal
Protocol, the timing of withdrawal
complicates any recognition by the
Parties of this development for 2013. In
addition, as detailed below, carryover
for 2012 is zero and EPA is not
proposing reductions on that basis. EPA
is therefore proposing to allocate
562,326 kg, the full amount authorized
by the Parties, in particular due to the
loss of iodomethane. EPA welcomes
comment on the proposed levels of
exempted new production and import
for critical uses and the amount of
material that may be sold from prephaseout inventory for critical uses.
1. Approach for Determining Critical
Stock Allowances
EPA is proposing a new approach for
determining the amount of CSAs and
CUAs to allocate. EPA is proposing to
calculate ‘‘available stocks’’ as a
percentage of the existing inventory, as
was reported to EPA on January 1, 2012.
Under this approach, EPA is soliciting
comment on two different amounts of
‘‘available stocks’’, and thus two
different possible allocations of CSAs.
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EPA is also soliciting comment on a
separate approach that would continue
to use the framework methodology to
calculate the amount of ‘‘available
stocks’’ by estimating drawdown during
2012 and providing for a supply chain
factor for 2013. As noted above, EPA is
proposing to not reduce the critical use
authorization of the Parties, and thus is
proposing that any authorized amount
not allocated as CSAs be allocated as
new production and import allowances.
In past CUE allocation rules, EPA
allocated CSAs in amounts that
represented not only the difference
between the total authorized CUE
amount and the amount of authorized
new production and import but also an
additional amount to reflect available
stocks. After determining the CSA
amount, EPA determined the portion of
CUE methyl bromide to come from new
production and import such that the
total amount of methyl bromide
exempted for critical uses did not
exceed the total amount authorized by
the Parties for that year.
EPA views the decision whether to
include these additional amounts in the
calculation of the year’s overall CSA
level as an appropriate exercise of
discretion. The Agency is not required
to allocate the full amount of authorized
new production and consumption. The
Parties only agree to ‘‘permit’’ a
particular level of production and
consumption; they do not—and
cannot—mandate that the United States
authorize this level of production and
consumption domestically. Nor does the
CAA require EPA to allow the full
amount permitted by the Parties.
Section 604(d)(6) of the CAA does not
require EPA to exempt any amount of
production and consumption from the
phaseout, but instead specifies that the
Agency ‘‘may’’ create an exemption for
critical uses, providing EPA with
substantial discretion.
When determining the CSA amounts,
EPA considers what portion of existing
stocks would be ‘‘available’’ for critical
uses during that control period. The
Parties to the Protocol recognized in
their Decisions that the level of existing
stocks may differ from the level of
available stocks. Decision XXIII/4 states
that ‘‘production and consumption of
methyl bromide for critical uses should
be permitted only if methyl bromide is
not available in sufficient quantity and
quality from existing stocks * * *.’’ In
addition, earlier Decisions refer to the
use of ‘‘quantities of methyl bromide
from stocks that the Party has
recognized to be available.’’ Thus, it is
clear that individual Parties have the
ability to determine their level of
available stocks. Decision XXIII/4
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further reinforces this concept by
including the phrase ‘‘minus available
stocks’’ as a footnote to the United
States’ authorized level of production
and consumption in Table B. Section
604(d)(6) of the CAA does not require
EPA to adjust the amount of new
production and import to reflect the
availability of stocks; however, as
explained in previous rulemakings,
making such an adjustment is a
reasonable exercise of EPA’s discretion
under this provision.
In recent CUE rules, EPA has
calculated the amount of ‘‘available
stocks’’ using a formula adopted in the
2008 CUE rule: ASCP =
ESPP¥DPP¥SCFCP, where ASCP would
be the available stocks on the first day
of the control period; ESPP would be the
existing pre-phaseout stocks of methyl
bromide held in the United States by
producers, importers, and distributors
on the first day of the prior control
period; DPP would be the estimated
drawdown of existing stocks during the
prior control period; and SCFCP would
be the supply chain factor for the
control period. In the section below,
EPA is taking comment on using this
approach, and is alternatively proposing
a new approach, for determining the
amount of available stocks.
Option 1: Percentage of Existing
Inventory
For 2013, EPA is proposing a new
approach that would allocate critical
stock allowances in an amount equal to
a percentage of the existing inventory.
Under this approach, EPA proposes to
calculate ‘‘available stocks’’ as a
percentage of the existing inventory, as
was reported to EPA on January 1, 2012.
EPA is considering alternate approaches
for allocating critical stock allowances
because the old approach, discussed as
option 2 below, may be increasingly
inaccurate as the amount of inventory
declines, overly complex, and
contributing to delay in issuing the final
critical use exemption. Furthermore,
EPA believes that efforts to in estimate
available inventory may be further
complicated for 2013 by the recent
withdrawal of iodomethane from the
market.
In the 2012 Final Rule, EPA
recognized ‘‘that its estimates [of
available stocks] have become
increasingly inexact in characterizing
actual drawdown of pre-phaseout
inventory, as the amounts in inventory
have declined over time. EPA intends to
consider the adequacy of using this
formula to assess ‘available stocks’ in a
future action.’’ Initially, the drawdown
estimate was a simple linear model
based on past years’ rates. EPA modified
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the approach when it became apparent
that the inventory drawdown was
decreasing exponentially rather than
linearly. EPA noted in the 2009 CUE
Rule that the rate of drawdown was
based mostly on the business decisions
of the companies that hold pre-phaseout
inventory, and included aspects that are
difficult for EPA to know or quantify,
such as honoring long-term
relationships with non-CUE customers
or holding inventory in response to
price fluctuations. To refine the analysis
in subsequent rules EPA separately
analyzed the use of inventory on critical
uses, for which there are a set number
of allowances, and non-critical uses, for
which there are not. This approach is
discussed in more detail below.
Despite increased specificity, precise
estimates still proved elusive. In
successive years, EPA substantially
overestimated inventory drawdown.
Most recently, in the 2012 Rule, EPA
estimated a drawdown of 1,110,633 kg,
when the actual drawdown was half
that amount, or 556,794 kg. The results
of the methodology using the updated
data were sufficiently different that EPA
considered providing additional notice
and the opportunity to comment to
incorporate them into the final
allocation rule. EPA is concerned that as
the total amount of both the U.S.
authorization and the pre-phaseout
stocks become smaller, efforts to perfect
EPA estimates in this area will delay
needed rulemaking.
Moreover, EPA believes that the fact
that its projections consistently overestimate the amount of inventory that
will be drawn down is evidence that
EPA has been substantially overestimating the availability of prephaseout stocks. EPA has received
comments in past rulemakings that
existing inventory was not actually
available to users because of reductions
in the number of distributors, and
decisions by distributors not to sell
inventory. While EPA believes it is
appropriate to rely on market flexibility
and efficiency to distribute existing
stocks of inventory, EPA recognizes that
the data appear to show that inventory
is less ‘‘available’’ than was estimated
under EPA’s prior approach.
EPA believes problems with the
existing formula may also become worse
due to a recent change in the geographic
distribution of critical users. In the past,
EPA has considered all pre-phaseout
inventory to be available to all users,
regardless of location. This assumption,
as discussed in the 2009 CUE rule (74
FR 19887, April 30, 2009), was based on
the fact that inventory is held in
California and the Southeast, as well as
other locations around the country.
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While the geographic distribution of
inventory generally remains the same,
the authorized critical uses have shifted
to California over the last two years. In
the 2011 control period, 49% of the total
authorization was for pre-plant uses in
California and 38% was for pre-plant
uses in the Southeast. In 2013, this ratio
will be 91% and 4% respectively.1
EPA believes that inventory held in
the Southeast may not be equally
available to critical users in California.
Stakeholders have told EPA that
distributors do not ship pre-phaseout
inventory to buyers across the country.
Unlike newly produced or imported
material which enters nationwide
distribution networks, inventory is
mostly held by regional distributors. In
addition, those distributors typically
sell both the gas and the application
services together. Distributors would
therefore incur additional expense to
ship material without being able to
charge for performing the application.
EPA specifically encourages comment
on the question of whether inventory
held in one part of the country has been,
or can be, transported to critical uses in
another part of the country.
Another reason EPA is proposing to
allocate critical stock allowances equal
to a percentage of the existing inventory
is that EPA believes this method will be
easier to calculate and will help
streamline the issuance of the CUE
allocation rule. EPA has received
comment in the past few CUE Rules that
the agency should find ways to issue the
allocation rulemakings before the start
of the control period. In the 2012 CUE
final rule, EPA stated that the agency
‘‘will consider means of streamlining
the Critical Use Exemption rulemaking
in the future so that the rule can be
issued prior to the start of the control
period.’’ Absent that, EPA will seek to
issue a final rule as soon into the control
period as possible. EPA is concerned
that efforts to correct estimates and
incorporate the most recent data into the
calculation of the supply chain factor
and the rest of the formula will further
delay future CUE rules. EPA recognized
in the 2012 Rule that ‘‘the time-sensitive
need for a CUE authorization for the
current calendar year and concluded
that re-opening the allocation for
comment is not warranted.’’ EPA
1 EPA treats company-specific methyl bromide
inventory information as confidential and believes
that disaggregating the inventory data by geographic
area could potentially reveal CBI. EPA solicits
comment on this issue but is not proposing at this
time to release data showing how much inventory
is located in or near California. However, even in
the absence of specific inventory data broken down
by region, EPA believes that the fact that over 90%
of critical use is in California is relevant to judging
the availability of existing stocks.
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74441
believes that its prior formula may have
attempted to achieve greater precision
than was possible or needed, especially
in light of the continued reduction in
both inventory and annual
authorizations for critical uses. Thus,
EPA is considering an alternate
approach, which provides a greater
likelihood of expediting the rulemaking
process. EPA will continue to consider
other possible means of streamlining the
CUE rulemaking process in the future.
As part of this approach, EPA would
end its use of the supply chain factor
(SCF).2 Because this approach does not
use the available stocks calculation
developed in the 2008 CUE Rule to
determine the amount of available
stocks for use by critical users in 2013,
calculation of the SCF is unnecessary.
EPA notes that the entire critical use
exemption authorized by the Parties for
2013 is 562 MT, which is substantially
less than the existing inventory. EPA
believes that, although portions of the
existing inventory may not practically
be available under usual circumstances
(e.g., because it may be located in the
Southeast and not California), users may
be able to access greater amounts of
inventory in the event of extraordinary
circumstances such as a catastrophic
domestic production failure.
In addition to soliciting comment on
this approach to calculating CSAs, EPA
is also soliciting comment on the
specific amount of inventory to be
allocated. EPA is proposing to allocate
CSAs equal to 5% of the January 1,
2012, reported inventory. Alternatively,
EPA is also taking comment on not
allocating any CSAs for 2013 under this
approach in light of the effect that the
withdrawal of iodomethane may have
on the demand for inventory. The two
options are discussed below.
EPA is proposing to allocate CSAs
equal to 5% of the January 1, 2012,
reported inventory. The inventory at
that date was 1,248,876 kg. Therefore,
under this approach, EPA would
allocate 62,444 kg of critical stock
allowances for 2013. Since 2006, the
amount of prior year inventory used
through the expenditure of CSAs has
ranged from 8% to 26%. EPA believes
that it would be appropriate to select a
percentage that is below the historic
range for several reasons. First, EPA
wishes to ensure that the amount
allocated for 2013 will be available to
critical users in that year. As discussed
above, the availability of existing
inventory is becoming increasingly
difficult to estimate as the amount
2 The purpose, and calculation, of the supply
chain factor is discussed in greater detail below,
and in prior CUE notices.
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declines. Although EPA is proposing to
consider historic patterns of availability
in considering how many CSAs to
allocate, the fact that stocks in the
Southeast may be unavailable as a
practical matter for growers in
California, while critical uses have
recently become highly concentrated in
California, suggests that, even under this
approach, a conservative approach to
estimating availability of inventory is
warranted. As noted above, this issue is
particularly important for 2013 because
the unexpected withdrawal of
iodomethane.
EPA believes it is reasonable to
assume that 5% of existing inventory on
January 1, 2012, could be available for
critical users in 2013. Historically, the
drawdown of inventory for all uses has
never exceeded 42% of the prior year’s
inventory. Drawdown would have to be
over twice that rate in 2012 for there to
be less inventory in 2013 than the
amount of the proposed CSA. Rather,
EPA anticipates that the constraints on
drawdown discussed in prior rules (e.g.,
critical uses capped by allocation
amounts, revised labeling removing
uses, increased value of the material as
supply decreases) will continue to limit
the drawdown in 2012. At the same
time, expenditure of CSAs have never
amounted to less than 8% of inventory,
and even if inventory was purchased for
critical uses at only half that rate, it
would still amount to 4% of the existing
inventory, so EPA anticipates that at
least that much inventory could be
available for critical uses during 2013.
EPA is also seeking comment on using
the above approach but allocating 0%
from existing stocks for 2013 in light of
the withdrawal of iodomethane from the
market. In March 2012, Arysta
LifeScience, the manufacturer of
iodomethane, suspended the sale of
iodomethane across the United States.
This alternative was registered for use in
48 states on strawberries, tomatoes,
peppers, ornamentals, turf, orchard
replant, forest nursery seedlings, and
strawberry nurseries. Many users had
been transitioning to this alternative
since 2008, when the product was
federally registered.
EPA believes that the unanticipated
loss of this alternative could have
increased demand for methyl bromide
in 2012 from critical users. In comments
to EPA’s 2010 CUE Rule, Arysta
provided data that 97,341 kg of
iodomethane was used in 2008 and
177,991 kg was used in 2009. They
calculated this to be equivalent to
approximately 5,000 and 10,000 acres
respectively. They also anticipated sales
of 250,000 kg in 2010, which would be
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equivalent to 650 MT of methyl bromide
on 13,500 acres.
In 2012, critical users may seek
additional methyl bromide from prephaseout inventory than in previous
years. The 2012 critical uses include all
of the registered uses of iodomethane
except for turf. Growers in Florida and
the Southeastern United States were
using iodomethane on tomatoes,
peppers, strawberries, and ornamentals.
While many of these sectors could use
alternatives other than iodomethane,
such as the UGA 3-way, the unexpected
loss of iodomethane could lead to
growers using inventory methyl
bromide for this season. The historical
trend described below, in which no
more than 70% of the CSAs allocated in
one year had ever been expended, may
not hold true for 2012. However, under
the framework, the use of inventory for
critical uses cannot exceed the total
CSA allocation of 263 MT in 2012.
EPA also does not believe that the
withdrawal of iodomethane will
increase demand for pre-phaseout
inventory from non-critical uses in
2012. Under the reregistration decision
for methyl bromide, seven non-critical
uses remain on the pre-plant methyl
bromide labels. These non-critical uses
can continue to use methyl bromide but
are restricted to pre-phaseout inventory.
The uses are caneberries, fresh market
tomatoes grown in California, fresh
market peppers grown in California,
Vidalia onions grown in Georgia, ginger
grown in Hawaii, soils on golf courses
and athletic/recreational fields for
resurfacing/replanting of turf, and
tobacco seedling trays. See 76 FR 7200
(February 9, 2011). Collectively they are
referred to as ‘‘Group II uses.’’ Of the
Group II uses, iodomethane was only
registered for use on fresh market
tomatoes grown in California, fresh
market peppers grown in California, and
turf. Iodomethane was not used in
California and EPA suspects it was not
widely used on turf since that sector did
not submit an application for a critical
use exemption for 2015. EPA is seeking
comment and additional data on
whether the loss of iodomethane will
limit the availability of inventory in
2013.
EPA understands that changes in the
status of methyl bromide alternatives
can occur, and that these changes may
expand or contract the list of existing
options. We also understand that the
sudden change in the availability of
iodomethane has created near-term
difficulties for growers in transition. As
noted above, EPA has taken this change
in circumstance into account in
proposing to allocate the full amount of
CUE authorized by the Parties in 2013.
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EPA is also requesting comment on a
range of potential amounts for the CSA
allocation, recognizing that past CUE
rules may have overestimated the
amount of stocks that are available to
critical users. Finally, EPA requests
comment on and relevant data to
support consideration of other potential
mechanisms within the Clean Air Act or
other statutory authorities that the EPA
could use to respond to unforeseen or
emergency situations.
Therefore, under this proposed
approach, the agency is proposing to
allocate 5% of existing inventory, or
62,444 kg of critical stock allowances for
2013. EPA solicits comment on whether
5% is the appropriate amount, or
whether a higher or lower figure would
be appropriate. EPA specifically seeks
comment on allocating 0 kg from stocks
under this approach. In considering the
possibility of an allocation for CSAs set
at 0 kg, EPA is particularly interested in
comments from critical stock allowance
holders who would be barred under the
existing framework from selling
inventory to critical users in 2013. EPA
is interested in learning whether an
allocation at or close to 0 kg would
prevent the drawdown of stocks or
prevent the fulfillment of contracts or
commitments to sell pre-phaseout
inventory in 2013. EPA is interested in
learning whether critical users who in
the past have accessed allocations of
CSAs would still be able to access
methyl bromide, either through the
conversion of CUAs to CSAs, or from
other sources. Finally, EPA is interested
in comment on the restriction in the
framework rule that limits the sale of
inventory to critical uses through the
CSA allocation, see 40 CFR 82.4(p),
whether that restriction should be lifted,
and to what extent reporting and
recordkeeping requirements should be
adjusted were the restriction lifted.
Option 2: Framework Approach
EPA also solicits comment on
whether it should retain for 2013 its
recent approach to calculating
‘‘available stocks’’ using the formula
ASCP = ESPP ¥ DPP ¥ SCFCP. EPA
calculates through this formula that
there will be 221,495 kg of ‘‘available
stocks’’ on January 1, 2013. Under this
approach, EPA would allocate 221,495
kg of CSAs for 2013.
The first step in the formula is to
estimate the drawdown of stocks during
2012. To do so, EPA adds the estimated
amount of CSAs that will be expended
in 2012 plus the estimated amount of
methyl bromide that will be used in
2012 for non-critical uses. EPA believes
that this is a better practice than using
a simple linear fit estimation, which
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was the approach EPA used in the first
few years it conducted this analysis. A
linear estimate would have projected
that no methyl bromide would remain
in inventory at the beginning of 2013.
Furthermore, this estimate does not
consider that the use of inventory on
critical uses is limited by the allocation
of CSAs.
The first element of the drawdown
estimate is the amount of inventory
used in 2012 on critical uses. This can
be no more than the number of CSAs
EPA allocated in the 2012 CUE Rule,
which is 263,082 kg. As discussed in the
Technical Support Document, on
average only 59% of the CSAs allocated
for a control period are reported as sold
in that control period. To estimate the
number of expended CSAs in 2012, EPA
conservatively assumes that 70% of the
CSAs allocated for 2012 will be sold.
This amount is greater than any year’s
use of CSA allocations, however EPA
notes below that the loss of
iodomethane may result in greater
demand for inventory in 2012 than past
years. Thus, EPA estimates that 184,157
kg of inventory will be sold for critical
uses in 2012.
The second element of the drawdown
estimate is the amount of inventory
used in 2012 on Group II and noncritical uses. Group II uses are seven
non-critical uses that remain on the preplant methyl bromide labels. Postharvest labels have not been revised yet
to implement the terms of the
reregistration decision concerning use of
methyl bromide for commodity
fumigation and thus the universe of
labeled post-harvest uses remains
broader.
There is no clear trend in the pattern
of usage for non-critical uses. EPA
therefore is estimating the amount of
sales for non-critical uses in 2012 by
analyzing the percent of the total
inventory used each year for this
purpose. For example, in 2010, 36% of
the total start of year inventory was sold
for non-critical uses. On a weight basis,
this was equal to 647 MT. In 2006,
much more inventory (on a weight
basis) was sold for non-critical uses,
1,249 MT, but this comprised only 16%
of the total start of year inventory that
year. EPA does not believe that an
average of the amounts sold (on a
weight basis) in 2006–2011 for all noncritical uses is accurate because the
inventory has declined. For example,
the 1,249 MT of inventory was sold in
2006 for non-critical uses is unlikely to
provide an accurate description of the
drawdown in 2012, even when averaged
with other years’ data, because there
was only 1,249 MT of inventory at the
beginning of 2012. EPA therefore is
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analyzing the drawdown on a
proportional basis rather than a strictly
weight basis. While the average
proportion is 17%, EPA is
conservatively using the highest
proportion. Therefore, EPA estimates
that 36% of the total start of year
inventory would be used for non-critical
uses in 2012. Thus, EPA estimates that
449,595 kg of inventory will be sold for
Group II uses in 2012. EPA believes that
this estimate is conservative because the
analysis encompasses years where the
use of inventory included all noncritical uses, and was not restricted to
Group II uses. These data are contained
in EPA’s annual Accounting
Frameworks submitted to UNEP and
summarized in the technical support
document in the docket.
In summary, EPA estimates the
drawdown of inventory in 2012 as the
sum of (1) the use of CSAs in 2012 and
(2) the estimate for non-critical uses in
2012. Using this method, EPA
conservatively projects that the prephaseout methyl bromide inventory will
be drawn down by 633,759 kg (184,157
+ 449,595) during 2012. This would
result in a pre-phaseout inventory
declining from 1,248,876 kg on January
1, 2012, to 615,124 kg on January 1,
2013. EPA welcomes comment on this
proposed method of calculating
inventory drawdown. If EPA utilizes
this approach in the final rule and
receives actual end-of-year reported data
on inventory levels before this rule is
finalized, EPA may substitute that data
for this estimate.
The next element in the calculation of
available stocks is the supply chain
factor (SCF). The SCF represents EPA’s
technical estimate of the amount of prephaseout inventory that would be
adequate to meet a need for critical use
methyl bromide after an unforeseen
domestic production failure. As
described in the 2008 CUE Rule, and the
Technical Support Document contained
in the docket to this rule, EPA estimates
that it would take 15 weeks for
significant imports of methyl bromide to
reach the U.S in the event of a major
supply disruption. Consistent with the
regulatory framework used in previous
CUE allocation rules, the SCF for 2013
conservatively reflects the effect of a
supply disruption occurring in the peak
period of critical use methyl bromide
production, which is the first quarter of
the year. While this 15-week disruption
is based on shipping capacity and does
not change year to year, other inputs to
EPA’s analysis do change each year
including the total U.S. and global
authorizations for methyl bromide and
the average seasonal production of
critical use methyl bromide in the
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United States. Using updated numbers,
EPA estimates that critical use
production in the first 15 weeks of each
year (the peak supply period) currently
accounts for approximately 70% of
annual critical use methyl bromide
demand. EPA, therefore, estimates that
the peak 15-week shortfall in 2013
could be 394 MT.
As EPA stated in previous CUE Rules,
the SCF is not a ‘‘reserve’’ of methyl
bromide but is merely an analytical tool
used to provide greater transparency
regarding how the Agency determines
CSA amounts. Further general
discussion of the SCF is in the final
2008 CUE rule (72 FR 74118, December
28, 2007) and further detail about the
analysis used to derive the value for the
2013 supply chain factor is provided in
the Technical Support Document
available on the public docket for this
rulemaking.
Using the formula AS2013 =
ES2012¥D2012¥SCF2013, EPA estimates
under the framework approach that
there will be 221,495 kg of pre-phaseout
stocks of methyl bromide ‘‘available’’ to
be allocated in 2013. (221,495 =
1,248,876 ¥ 633,759 ¥ 393,628). EPA
welcomes comment on this approach to
determining the level of available stocks
and the critical stock allowance
allocation for 2013.
In summary, EPA is proposing for
2013 a new approach for allocating
amounts authorized for critical uses
between CSAs and CUAs, by allocating
CSAs as a percentage of the existing
inventory. In particular, EPA is
proposing to allocate CSAs in an
amount equal to 5% of the 2012
reported inventory, or 62,444 kg. EPA
seeks comment on a range of values for
the allocation of CSAs, given the loss of
iodomethane. EPA particularly solicits
comment on allocating 0 kg of CSAs.
EPA is also seeking comment on using
the existing framework to calculate the
amount of ‘‘available stocks’’ in 2013.
EPA estimates the CSA allocation would
be 221,495 kg under this approach.
As in past years, EPA would allocate
CSAs based on each company’s
proportionate share of the aggregate
inventory. In 2006, the United States
District Court for the District of
Columbia upheld EPA’s treatment of
company-specific methyl bromide
inventory information as confidential.
NRDC v. Leavitt, 2006 WL 667327
(D.D.C. March 14, 2006). Therefore, the
documentation regarding companyspecific allocation of CSAs is in the
confidential portion of the rulemaking
docket and the individual CSA
allocations are not listed in the table in
40 CFR 82.8(c)(2). EPA will inform
listed companies of their CSA
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publication of the final rule.
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2. Approach for Determining New
Production and Import Allowances
For 2013, EPA is proposing to
generally apply the existing framework
established in the Framework Rule.
Under this approach, the amount of new
production would equal the total
amount authorized by the Parties to the
Montreal Protocol in Decision XXIII/4,
minus the CSA amount detailed above,
minus any reductions for carryover and
the uptake of alternatives. As explained
above, EPA has considered a number of
factors in determining the total
allocation, including the loss of the
alternative iodomethane, and is not
proposing to reduce the total allocation
below the amount approved in Decision
XXIII/4. Applying this established
approach, EPA is proposing to exempt
limited amounts of new production and
import of methyl bromide for critical
uses in 2013 such that the total
authorization equals 562,326 kg.
Because EPA is taking comment on a
range of values for the critical stock
allocation, there would be a
corresponding range of values for the
new production/import amount from to
340,831 kg to 562,326 kg. EPA is
proposing an approach that would
result in an allocation of 499,882 kg.
EPA is taking comment on this
approach.
Carryover Material The Parties in
paragraph 6 of Decision XXIII/4 ‘‘urge
parties operating under critical-use
exemptions to put in place effective
systems to discourage the accumulation
of methyl bromide produced under the
exemption.’’ As discussed in the
Framework Rule, EPA regulations
prohibit methyl bromide produced or
imported after January 1, 2005, under
the critical use exemption being added
to the existing pre-2005 inventory.
Quantities of methyl bromide produced,
imported, exported, or sold to end-users
under the critical use exemption in a
control period must be reported to EPA
the following year. EPA uses these
reports to calculate the amount of
methyl bromide produced or imported
under the critical use exemption, but
not exported or sold to end-users in that
year. EPA deducts an amount equivalent
to this ‘‘carryover’’ from the total level
of allowable new production and import
in the year following the year of the data
report. Carryover material (which is
produced using critical use allowances)
is not included in EPA’s definition of
existing inventory (which applies to
pre-2005 material) because this would
lead to a double-counting of carryover
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amounts, and a double reduction of
critical use allowances (CUAs).
All critical use methyl bromide that
companies reported to be produced or
imported in 2011 was sold to end users.
The information reported to EPA is that
1,499 MT of critical use methyl bromide
was produced or imported in 2011.
Slightly more than the amount
produced or imported was actually sold
to end-users. This additional amount
was from distributors selling material
that was carried over from the prior
control period. Using the existing
framework, EPA is proposing to apply
the carryover deduction of 0 kg to the
new production amount. EPA’s
calculation of the amount of carryover at
the end of 2011 is consistent with the
method used in previous CUE rules, and
with the method agreed to by the Parties
in Decision XVI/6 for calculating
column L of the U.S. Accounting
Framework. Past U.S. Accounting
Frameworks, including the one for 2011,
are available in the public docket for
this rulemaking.
Uptake of Alternatives Under the
existing framework, EPA considers data
on the availability of alternatives that it
receives following submission of each
nomination to UNEP. In previous rules
EPA has reduced the total CUE amount
when a new alternative has been
registered. Because EPA determines the
CSA allocation separately, any
reduction in the total amount has been
reflected in a corresponding reduction
in the allocation for new production/
import. However, where an alternative
is withdrawn, EPA cannot propose to
increase the total CUE amount above the
amount authorized by the Parties.
A development since the USG
submitted the 2013 CUN is that
Dimethyl Disulfide (DMDS) has been
registered in additional states. In July
2010, EPA registered DMDS to control
nematodes, weeds, and pathogens in
tomatoes, peppers, eggplants,
curcurbits, strawberries, ornamentals
and forest nursery seedlings, and
onions. The CUN considered only a
limited uptake in 2013. At that time
only a few states had registered DMDS
and it was not registered in either
California or Florida. Twenty-four states
have now registered DMDS, including
Georgia and Florida.
EPA is proposing not to make a
reduction to the new production/import
allocation based on these additional
state registrations. As discussed above,
over 90% of the amount authorized is
for critical uses in California, which has
not yet registered DMDS. EPA
anticipates that the uptake of DMDS in
the Southeast will therefore not
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significantly affect total demand for
critical use methyl bromide.
EPA is not proposing to make any
other modifications for alternatives.
Transition rates for other alternatives
have already been applied for
authorized 2013 critical use amounts
through the nomination and
authorization process. EPA will
consider new data received during the
comment period and continues to gather
information about methyl bromide
alternatives through the CUE
application process, and by other
means. EPA also continues to support
research and adoption of methyl
bromide alternatives, and to request
information about the economic and
technical feasibility of all existing and
potential alternatives.
Allocation Amounts EPA is proposing
to allocate 2013 critical use allowances
for new production or import of methyl
bromide equivalent to 499,882 kg.
Because EPA is proposing a range of
approaches for the critical stock
allocation, EPA is taking comment on
the corresponding range of values for
the new production/import amount
from to 340,831 kg to 562,326 kg.
EPA is proposing to allocate
allowances to the four companies that
hold baseline allowances. The proposed
allocation, as in previous years, is in
proportion to those baseline amounts, as
shown in the proposed changes to the
table in 40 CFR 82.8(c)(1). Paragraph 3
of Decision XXIII/4 states ‘‘that parties
shall endeavor to license, permit,
authorize or allocate quantities of
methyl bromide for critical uses as
listed in table A of the annex to the
present decision.’’ This is similar to
language in prior Decisions authorizing
critical uses. These Decisions call on
Parties to endeavor to allocate critical
use methyl bromide on a sector basis.
The Framework Rule proposed several
options for allocating critical use
allowances, including a sector-by-sector
approach. The agency evaluated various
options based on their economic,
environmental, and practical effects.
After receiving comments, EPA
determined that a lump-sum, or
universal, allocation, modified to
include distinct caps for pre-plant and
post-harvest uses, was the most efficient
and least burdensome approach that
would achieve the desired
environmental results, and that a sectorby-sector approach would pose
significant administrative and practical
difficulties. For the reasons discussed in
the preamble to the 2009 CUE rule (74
FR 19894), the agency believes that
under the approach adopted in the
Framework Rule, the actual critical use
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will closely follow the sector breakout
listed in the Parties’ decisions.
F. The Criteria in Decisions IX/6 and Ex.
I/4
Paragraphs 1 and 4 of Decision XXIII/
4 request Parties to ensure that the
conditions or criteria listed in Decisions
Ex. I/4 and IX/6, paragraph 1, are
applied to exempted critical uses for the
2013 control period. A discussion of the
agency’s application of the criteria in
paragraph 1 of Decision IX/6 appears in
sections V.A., V.D., and V.E. of this
preamble. In section V.D. the agency
solicits comments on the technical and
economic basis for determining that the
uses listed in this proposed rule meet
the criteria of the critical use exemption.
The CUNs detail how each proposed
critical use meets the criteria listed in
paragraph 1 of Decision IX/6, apart from
the criterion located at (b)(ii), as well as
the criteria in paragraphs 5 and 6 of
Decision Ex. I/4.
The criterion in Decision IX/
6(1)(b)(ii), which refers to the use of
available stocks of methyl bromide, is
addressed in section V.E. of this
preamble. The agency has previously
provided its interpretation of the
criterion in Decision IX/6(1)(a)(i)
regarding the presence of significant
market disruption in the absence of an
exemption, and EPA refers readers to
the 2006 CUE final rule (71 FR 5989,
February 6, 2006) as well as to the
memo on the docket ‘‘Development of
2003 Nomination for a Critical Use
Exemption for Methyl Bromide for the
United States of America’’ for further
elaboration.
The remaining considerations,
including the lack of available
technically and economically feasible
alternatives under the circumstance of
the nomination; efforts to minimize use
and emissions of methyl bromide where
technically and economically feasible;
the development of research and
transition plans; and the requests in
Decision Ex. I/4(5) and (6) that Parties
consider and implement MBTOC
recommendations, where feasible, on
reductions in the critical use of methyl
bromide and include information on the
methodology they use to determine
economic feasibility, are addressed in
the nomination documents.
Some of these criteria are evaluated in
other documents as well. For example,
the United States has further considered
matters regarding the adoption of
alternatives and research into methyl
bromide alternatives, criterion (1)(b)(iii)
in Decision IX/6, in the development of
the National Management Strategy
submitted to the Ozone Secretariat in
December 2005, updated in October
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2009, as well as in ongoing
consultations with industry. The
National Management Strategy
addresses all of the aims specified in
Decision Ex.I/4(3) to the extent feasible
and is available in the docket for this
rulemaking.
There continues to be a need for
methyl bromide in order to conduct the
research required by Decision IX/6. A
common example is an outdoor field
experiment that requires methyl
bromide as a standard control treatment
with which to compare the trial
alternatives’ results. As discussed in the
preamble to the 2010 CUE rule (75 FR
23179, May 3, 2010), research is a key
element of the critical use process.
Research on the crops shown in the
table in Appendix L to subpart A
remains a critical use of methyl
bromide. While researchers may
continue to use newly produced
material for field, post-harvest, and
emission minimization studies requiring
the use of methyl bromide, EPA
encourages researchers to use prephaseout inventory purchased through
the expenditure of CSAs. EPA also
encourages distributors to make
inventory available to researchers, to
promote the continuing effort to assist
growers to transition critical use crops
to alternatives.
G. Emissions Minimization
Previous decisions have stated that
critical users shall employ emission
minimization techniques such as
virtually impermeable films, barrier film
technologies, deep shank injection and/
or other techniques that promote
environmental protection, whenever
technically and economically feasible.
EPA developed a comprehensive
strategy for risk mitigation through the
2006 Reregistration Eligibility Decision
(RED) for methyl bromide, which is
implemented through restrictions on
how methyl bromide products can be
used. This approach requires that
methyl bromide labels include
directions that treated sites be tarped
except for California orchard replant
where EPA instead requires deep (18
inches or greater) shank applications.
The RED also incorporated incentives
for applicators to use high-barrier tarps,
such as virtually impermeable film
(VIF), by allowing smaller buffer zones
around those sites. In addition to
minimizing emissions, use of highbarrier tarps has the benefit of providing
pest control at lower application rates.
The amount of methyl bromide
nominated by the United States reflects
the lower application rates necessary
when using high-barrier tarps, where
such tarps are allowed.
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74445
EPA will continue to work with the
U.S. Department of Agriculture—
Agricultural Research Service (USDA–
ARS) and the National Institute for Food
and Agriculture (USDA–NIFA) to
promote emission reduction techniques.
The federal government has invested
substantial resources into best practices
for methyl bromide use, including
emission reduction practices. The
Cooperative Extension System, which
receives some support from USDA–
NIFA provides locally appropriate and
project focused outreach education
regarding methyl bromide transition
best practices. Additional information
on USDA research on alternatives and
emissions reduction can be found at:
https://www.ars.usda.gov/research/
programs/programs.htm?NP_CODE=308
and https://www.csrees.usda.gov/fo/
methylbromideicgp.cfm.
Users of methyl bromide should
continue to make every effort to
minimize overall emissions of methyl
bromide to the extent consistent with
State and local laws and regulations.
EPA also encourages researchers and
users who are using such techniques to
inform EPA of their experiences and to
provide such information with their
critical use applications.
VI. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
Under Executive Order (EO) 12866
(58 FR 51735, October 4, 1993), this
proposal is a ‘‘significant regulatory
action.’’ This action is likely to result in
a rule that may raise novel legal or
policy issues. Accordingly, EPA
submitted this action to the Office of
Management and Budget (OMB) for
review under Executive Orders 12866
and 13563 (76 FR 3821, January 21,
2011) and any changes made in
response to interagency
recommendations have been
documented in the docket for this
action.
B. Paperwork Reduction Act
This action does not impose any new
information collection burden. The
application, recordkeeping, and
reporting requirements have already
been established under previous critical
use exemption rulemakings and this
action does not propose to change any
of those existing requirements. The
Office of Management and Budget
(OMB) has previously approved the
information collection requirements
contained in the existing regulations at
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40 CFR part 82 under the provisions of
the Paperwork Reduction Act, 44 U.S.C.
3501 et seq. and has assigned OMB
control number 2060–0482. The OMB
control numbers for EPA’s regulations
in 40 CFR are listed in 40 CFR part 9.
C. Regulatory Flexibility Act
The RFA generally requires an agency
to prepare a regulatory flexibility
analysis of any rule subject to noticeand-comment rulemaking requirements
under the Administrative Procedure Act
or any other statute unless the agency
certifies that the rule will not have a
significant economic impact on a
substantial number of small entities.
Small entities include small businesses,
small organizations, and small
governmental jurisdictions. For
purposes of assessing the impacts of this
rule on small entities, small entity is
defined as: (1) A small business as
defined by the Small Business
Administration’s regulations at 13 CFR
121.201 (see Table below); (2) a small
governmental jurisdiction that is a
government of a city, county, town,
school district or special district with a
population of less than 50,000; and (3)
a small organization that is any not-forprofit enterprise which is independently
owned and operated and is not
dominant in its field.
NAICS Small business size
standard (in number of
employees or millions of
dollars)
Category
NAICS code
SIC code
Agricultural production
1112—Vegetable and Melon farming .........
1113—Fruit and Nut Tree Farming .............
1114—Greenhouse, Nursery, and Floriculture Production.
0171—Berry Crops ......................................
0172—Grapes.
0173—Tree Nuts.
Storage Uses ..............
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Distributors and Applicators.
Producers and Importers.
115114—Postharvest Crop activities (except Cotton Ginning).
311211—Flour Milling .................................
311212—Rice Milling ..................................
493110—General Warehousing and Storage.
493130—Farm Product Warehousing and
Storage.
115112—Soil Preparation, Planting and
Cultivating.
325320—Pesticide and Other Agricultural
Chemical Manufacturing.
Agricultural producers of minor crops
and entities that store agricultural
commodities are categories of affected
entities that contain small entities. This
proposed rule would only affect entities
that applied to EPA for an exemption to
the phaseout of methyl bromide. In most
cases, EPA received aggregated requests
for exemptions from industry consortia.
On the exemption application, EPA
asked consortia to describe the number
and size distribution of entities their
application covered. EPA estimated that
3,218 entities petitioned EPA for an
exemption for the 2005 control period.
EPA revised this estimate in 2011 down
to 1,800 end users of critical use methyl
bromide. EPA believes that the number
continues to decline as growers cease
applying for critical uses. Since many
applicants did not provide information
on the distribution of sizes of entities
covered in their applications, EPA
estimated that, based on the above
definition, between one-fourth and onethird of the entities may be small
businesses. In addition, other categories
of affected entities do not contain small
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0175—Deciduous Tree Fruits (except apple
orchards and farms).
0179—Fruit and Tree Nuts, NEC.
0181—Ornamental Floriculture and Nursery
Products.
0831—Forest Nurseries and Gathering of
Forest Products.
......................................................................
$7 million.
2041—Flour and Other Grain Mill Products
2044—Rice Milling ......................................
4225—General Warehousing and Storage
500 employees.
500 employees.
$25.5 million.
4221—Farm Product Warehousing and
Storage.
0721—Crop Planting, Cultivation, and Protection.
2879—Pesticides and Agricultural Chemicals, NEC.
$25.5 million.
businesses based on the above
description.
After considering the economic
impacts of this proposed rule on small
entities, I certify that this action will not
have a significant economic impact on
a substantial number of small entities.
In determining whether a rule has a
significant economic impact on a
substantial number of small entities, the
impact of concern is any significant
adverse economic impact on small
entities, since the primary purpose of
the regulatory flexibility analyses is to
identify and address regulatory
alternatives ‘‘which minimize any
significant economic impact of the
proposed rule on small entities.’’ (5
U.S.C. 603–604). Thus, an agency may
certify that a rule will not have a
significant economic impact on a
substantial number of small entities if
the rule relieves a regulatory burden, or
otherwise has a positive economic effect
on all of the small entities subject to the
rule. Since this rule would allow the use
of methyl bromide for approved critical
uses after the phaseout date of January
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Fmt 4702
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$7 million.
500 employees.
1, 2005, this action would confer a
benefit to users of methyl bromide. EPA
estimates in the Regulatory Impact
Assessment found in the docket to this
rule that the reduced costs resulting
from the de-regulatory creation of the
exemption are approximately $22
million to $31 million on an annual
basis (using a 3% or 7% discount rate
respectively). We have therefore
concluded that this proposed rule
would relieve regulatory burden for all
small entities.
D. Unfunded Mandates Reform Act
This action contains no Federal
mandates under the provisions of Title
II of the Unfunded Mandates Reform
Act of 1995 (UMRA), 2 U.S.C. 1531–
1538 for State, local, or tribal
governments or the private sector. The
action imposes no enforceable duty on
any State, local or tribal governments or
the private sector. Instead, this action
would provide an exemption for the
manufacture and use of a phased out
compound and would not impose any
new requirements on any entities.
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Therefore, this action is not subject to
the requirements of sections 202 or 205
of the UMRA. This action is also not
subject to the requirements of section
203 of UMRA because it contains no
regulatory requirements that might
significantly or uniquely affect small
governments.
E. Executive Order 13132: Federalism
This action does not have federalism
implications. It will not have substantial
direct effects on the States, on the
relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. This proposed
rule is expected to primarily affect
producers, suppliers, importers, and
exporters and users of methyl bromide.
Thus, Executive Order 13132 does not
apply to this proposed rule. In the spirit
of Executive Order 13132, and
consistent with EPA policy to promote
communications between EPA and State
and local governments, EPA specifically
solicits comment on this proposed
action from State and local officials.
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). This rule does not significantly or
uniquely affect the communities of
Indian tribal governments nor does it
impose any enforceable duties on
communities of Indian tribal
governments. Thus, Executive Order
13175 does not apply to this action. EPA
specifically solicits additional comment
on this proposed action from tribal
officials.
G. Executive Order No. 13045:
Protection of Children From
Environmental Health and Safety Risks
EPA interprets EO 13045 (62 FR
19885, April 23, 1997) as applying only
to those regulatory actions that concern
health or safety risks, such that the
analysis required under section 5–501 of
the EO has the potential to influence the
regulation. This action is not subject to
EO 13045 because it does not establish
an environmental standard intended to
mitigate health or safety risks.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This proposed rule is not a
‘‘significant energy action’’ as defined in
Executive Order 13211, ‘‘Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use’’ (66 FR 28355 (May
22, 2001)) because it is not likely to
have a significant adverse effect on the
supply, distribution, or use of energy.
This proposed rule does not pertain to
any segment of the energy production
economy nor does it regulate any
manner of energy use. Therefore, we
have concluded that this proposed rule
is not likely to have any adverse energy
effects.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law
104–113, 12(d) (15 U.S.C. 272 note)
directs EPA to use voluntary consensus
standards in its regulatory activities
unless to do so would be inconsistent
with applicable law or otherwise
impractical. Voluntary consensus
standards are technical standards (e.g.,
materials specifications, test methods,
sampling procedures, and business
practices) that are developed or adopted
by voluntary consensus standards
bodies. NTTAA directs EPA to provide
Congress, through OMB, explanations
when the agency decides not to use
available and applicable voluntary
consensus standards. This proposed
rulemaking does not involve technical
standards. Therefore, EPA is not
considering the use of any voluntary
consensus standards.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order (EO) 12898 (59 FR
7629 (Feb. 16, 1994)) establishes federal
executive policy on environmental
justice. Its main provision directs
federal agencies, to the greatest extent
practicable and permitted by law, to
make environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
populations in the United States.
EPA has determined that this
proposed rule will not have
disproportionately high and adverse
human health or environmental effects
on minority or low-income populations,
because it affects the level of
environmental protection equally for all
affected populations without having any
disproportionately high and adverse
human health or environmental effects
on any population, including any
minority or low-income population.
Any ozone depletion that results from
this proposed rule will impact all
affected populations equally because
ozone depletion is a global
environmental problem with
environmental and human effects that
are, in general, equally distributed
across geographical regions in the
United States.
List of Subjects in 40 CFR Part 82
Environmental protection, Chemicals,
Exports, Imports, Ozone depletion.
Dated: December 7, 2012.
Lisa P. Jackson,
Administrator.
For the reasons stated in the
preamble, 40 CFR Part 82 is proposed to
be amended as follows:
PART 82—PROTECTION OF
STRATOSPHERIC OZONE
1. The authority citation for part 82
continues to read as follows:
Authority: 42 U.S.C. 7414, 7601, 7671–
7671q.
2. Amend § 82.8 by revising the table
in paragraph (c)(1) and by revising
paragraph (c)(2).
§ 82.8 Grant of essential use allowances
and critical use allowances.
*
*
*
(c) * * *
(1) * * *
mstockstill on DSK4VPTVN1PROD with
Great Lakes Chemical Corp. A Chemtura Company ..................................................................................
Albemarle Corp. ...........................................................................................................................................
ICL–IP America ............................................................................................................................................
TriCal, Inc. ...................................................................................................................................................
16:21 Dec 13, 2012
Jkt 229001
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*
2013 Critical use
allowances for
pre-plant uses*
(kilograms)
Company
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*
Fmt 4702
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E:\FR\FM\14DEP1.SGM
287,633
118,281
65,365
2,035
14DEP1
2013 Critical use
allowances for
post-harvest uses*
(kilograms)
16,145
6,639
3,669
114
74448
Federal Register / Vol. 77, No. 241 / Friday, December 14, 2012 / Proposed Rules
2013 Critical use
allowances for
pre-plant uses*
(kilograms)
Company
Total** ...................................................................................................................................................
2013 Critical use
allowances for
post-harvest uses*
(kilograms)
473,315
26,567
* For production or import of Class I, Group VI controlled substance exclusively for the Pre-Plant or Post-Harvest uses specified in appendix L
to this subpart.
** Due to rounding, numbers do not add exactly.
(2) Allocated critical stock allowances
granted for specified control period. The
following companies are allocated
critical stock allowances for 2013 on a
pro-rata basis in relation to the
inventory held by each.
Degesch America, Inc.
Helena Chemical Co.
ICL–IP America
Industrial Fumigant Company
Pacific Ag Supplies Inc.
Pest Fog Sales Corp.
Prosource One
Trical Inc.
Trident Agricultural Products
TriEst Ag Group, Inc.
Univar
Western Fumigation
Company
Albemarle
Bill Clark Pest Control, Inc.
Burnside Services, Inc.
Cardinal Professional Products
Chemtura Corp.
Crop Production Services
TOTAL¥62,444 kilograms
3. Appendix L to Subpart A is revised
to read as follows:
Appendix L to Subpart A of Part 82—
Approved Critical Uses and Limiting
Critical Conditions for Those Uses for
the 2013 Control Period
Column A
Column B
Column C
Approved critical uses
Approved critical user and location of use
Limiting critical conditions that exist, or that the approved critical
user reasonably expects could rise without methyl bromide
fumigation:
PRE-PLANT USES
Cucurbits .........................
Georgia growers on fewer than 10 acres ...............
Eggplant ..........................
(a) Florida growers ..................................................
(b) Georgia growers on fewer than 10 acres .........
Nursery Stock (Fruit, Nut,
Flower).
Orchard Replant .............
Ornamentals ...................
Members of the California Association of Nursery
and Garden Centers representing Deciduous
Tree Fruit Growers.
California stone fruit, table and raisin grape, wine
grape, walnut, and almond growers.
(a) California growers ..............................................
mstockstill on DSK4VPTVN1PROD with
(b) Florida growers ..................................................
Peppers ..........................
VerDate Mar<15>2010
(a) Florida growers ..................................................
16:21 Dec 13, 2012
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Moderate to severe yellow or purple nutsedge infestation.
Moderate to severe soilborne disease infestation.
Moderate to severe root knot nematode infestation.
Moderate to severe yellow or purple nutsedge infestation.
Moderate to severe soilborne disease infestation.
Restrictions on alternatives due to karst topographical.
features and soils not supporting seepage irrigation.
Moderate to severe yellow or purple nutsedge infestation.
Moderate to severe nematode infestation.
Moderate to severe pythium collar, crown and root rot.
Moderate to severe southern blight infestation.
Restrictions on alternatives due to karst topographical features.
Moderate to severe nematode infestation.
Medium to heavy clay soils.
Local township limits prohibiting 1,3-dichloropropene.
Moderate to severe nematode infestation.
Moderate to severe soilborne disease infestation.
Replanted orchard soils to prevent orchard replant disease.
Medium to heavy soils.
Local township limits prohibiting 1,3-dichloropropene.
Moderate to severe soilborne disease infestation.
Moderate to severe nematode infestation.
Local township limits prohibiting 1,3-dichloropropene.
Moderate to severe weed infestation.
Moderate to severe soilborne disease infestation.
Moderate to severe nematode infestation.
Restrictions on alternatives due to karst topographical.
features and soils not supporting seepage irrigation.
Moderate to severe yellow or purple nutsedge infestation.
Moderate to severe soilborne disease infestation.
Moderate to severe nematode infestation.
Restrictions on alternatives due to karst topographical.
features and soils not supporting seepage irrigation.
Sfmt 4700
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14DEP1
Federal Register / Vol. 77, No. 241 / Friday, December 14, 2012 / Proposed Rules
74449
Column A
Column B
Column C
Approved critical uses
Approved critical user and location of use
Limiting critical conditions that exist, or that the approved critical
user reasonably expects could rise without methyl bromide
fumigation:
(b) Georgia growers on fewer than 10 acres .........
Strawberry Fruit ..............
California growers ...................................................
Strawberry Nurseries ......
California growers ...................................................
Tomatoes ........................
(a) Florida growers ..................................................
(b) Georgia growers on fewer than 10 acres .........
Moderate to severe yellow or purple nutsedge infestation.
Moderate to severe nematode infestation, or moderate to severe pythium root and collar rots.
Moderate to severe southern blight infestation, crown or root
rot.
Restrictions on alternatives due to karst topographical features.
Moderate to severe black root rot or crown rot.
Moderate to severe yellow or purple nutsedge infestation.
Moderate to severe nematode infestation.
Local township limits prohibiting 1,3-dichloropropene.
Time to transition to an alternative.
Moderate to severe soilborne disease infestation.
Moderate to severe yellow or purple nutsedge infestation.
Moderate to severe nematode infestation.
Moderate to severe yellow or purple nutsedge infestation.
Moderate to severe soilborne disease infestation.
Moderate to severe nematode infestation.
Restrictions on alternatives due to karst topographical.
features and soils not supporting seepage irrigation.
Moderate to severe yellow or purple nutsedge infestation.
Moderate to severe soilborne disease infestation.
Moderate to severe nematode infestation.
Restrictions on alternatives due to karst topographical features.
POST-HARVEST USES
Food Processing .............
(a) Rice millers in the U.S. who are members of
the USA Rice Millers Association.
(b) Pet food manufacturing facilities in the U.S.
who are members of the Pet Food Institute.
(c) Members of the North American Millers’ Association in the U.S..
Commodities ...................
Dry Cured Pork Products
California entities storing walnuts, dried plums,
figs, raisins, and dates (in Riverside county
only) in California.
Members of the National Country Ham Association
and the Association of Meat Processors,
Nahunta Pork Center (North Carolina), and
Gwaltney and Smithfield Inc.
[FR Doc. 2012–30225 Filed 12–13–12; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 131
[EPA–HQ–OW–2009–0596; FRL–9759–1]
RIN 2040–AF41
Water Quality Standards for the State
of Florida’s Lakes and Flowing Waters;
Proposed Rule; Stay
Environmental Protection
Agency (EPA).
ACTION: Proposed rule; proposed stay.
mstockstill on DSK4VPTVN1PROD with
AGENCY:
SUMMARY: The Environmental Protection
Agency (EPA) proposes to temporarily
stay our regulation the ‘‘Water Quality
Standards for the State of Florida’s
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16:21 Dec 13, 2012
Jkt 229001
Moderate to severe beetle, weevil, or moth infestation.
Presence of sensitive electronic equipment subject to corrosion.
Time to transition to an alternative.
Moderate to severe beetle, moth, or cockroach infestation.
Presence of sensitive electronic equipment subject to corrosion.
Time to transition to an alternative.
Moderate to severe beetle infestation.
Presence of sensitive electronic equipment subject to corrosion.
Time to transition to an alternative.
Rapid fumigation required to meet a critical market window,
such as during the holiday season.
Red legged ham beetle infestation.
Cheese/ham skipper infestation.
Dermested beetle infestation.
Ham mite infestation.
Lakes and Flowing Waters; Final Rule’’
(inland waters rule) to November 15,
2013. EPA’s inland waters rule currently
includes an effective date of January 6,
2013, for the entire regulation except for
the site-specific alternative criteria
provision, which took effect on
February 4, 2011. This proposed stay of
its regulations is until November 15,
2013, does not affect or change the
February 4, 2011, effective date for the
site-specific alternative criteria
provision.
Comments must be received on
or before December 28, 2012.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
OW–2009–0596, by one of the following
methods:
1. https://www.regulations.gov: Follow
the on-line instructions for submitting
comments.
DATES:
PO 00000
Frm 00058
Fmt 4702
Sfmt 4702
2. Email: ow-docket@epa.gov.
3. Mail to: Water Docket, U.S.
Environmental Protection Agency, Mail
code: 28221T, 1200 Pennsylvania
Avenue NW., Washington, DC 20460,
Attention: Docket ID No. EPA–HQ–OW–
2009–0596.
4. Hand Delivery: EPA Docket Center,
EPA West Room 3334, 1301
Constitution Avenue NW., Washington,
DC 20004, Attention Docket ID No.
EPA–HQ–OW–2009–0596. Such
deliveries are only accepted during the
Docket’s normal hours of operation, and
special arrangements should be made
for deliveries of boxed information.
Instructions: Direct your comments to
Docket ID No. EPA–HQ–OW–2009–
0596. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at https://
www.regulations.gov, including any
E:\FR\FM\14DEP1.SGM
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Agencies
[Federal Register Volume 77, Number 241 (Friday, December 14, 2012)]
[Proposed Rules]
[Pages 74435-74449]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2012-30225]
[[Page 74435]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 82
[EPA-HQ-OAR-2010-0280; FRL-9714-4]
RIN 2060-AR41
Protection of Stratospheric Ozone: The 2013 Critical Use
Exemption From the Phaseout of Methyl Bromide
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: EPA is proposing uses that qualify for the 2013 critical use
exemption. EPA is also proposing to amend the regulatory framework to
determine the amount of methyl bromide that may be produced, imported,
or supplied from existing pre-phaseout inventory for those uses in
2013. EPA is taking action under the authority of the Clean Air Act to
reflect a recent consensus decision taken by the Parties to the
Montreal Protocol on Substances that Deplete the Ozone Layer at the
Twenty-Third Meeting of the Parties. EPA is seeking comment on the list
of critical uses and on EPA's determination of the specific amounts of
methyl bromide that may be produced and imported, or sold from pre-
phaseout inventory for those uses.
DATES: Comments must be submitted by January 28, 2013. Any party
requesting a public hearing must notify the contact person listed below
by 5 p.m. Eastern Standard Time on December 19, 2012. If a hearing is
requested it will be held on December 31, 2012. EPA will post
information regarding a hearing, if one is requested, on the Ozone
Protection Web site www.epa.gov/ozone/strathome.html. Persons
interested in attending a public hearing should consult with the
contact person below regarding the location and time of the hearing.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
OAR-2010-0280, by one of the following methods:
www.regulations.gov: Follow the on-line instructions for
submitting comments.
Email: a-and-r-Docket@epa.gov.
Fax: (202) 566-9744.
Phone: (202) 566-1742.
U.S. Mail: Docket EPA-HQ-OAR-2010-0280, U.S. Environmental
Protection Agency, EPA Docket Center, Air and Radiation Docket, Mail
Code 28221T, 1200 Pennsylvania Avenue NW., Washington, DC 20460.
Hand Delivery or Courier: Docket EPA-HQ-OAR-2010-0280, EPA
Docket Center--Public Reading Room, EPA West Building, Room 3334, 1301
Constitution Avenue NW., Washington, DC 20004. Such deliveries are only
accepted during the Docket's normal hours of operation, and special
arrangements should be made for deliveries of boxed information.
Instructions: Direct your comments to Docket ID No. EPA-HQ-OAR-
2010-0280. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
www.regulations.gov, including any personal information provided,
unless the comment includes information claimed to be Confidential
Business Information (CBI) or other information whose disclosure is
restricted by statute. Do not submit information that you consider to
be CBI or otherwise protected through www.regulations.gov or email. The
www.regulations.gov Web site is an ``anonymous access'' system, which
means EPA will not know your identity or contact information unless you
provide it in the body of your comment. If you send an email comment
directly to EPA without going through www.regulations.gov your email
address will be automatically captured and included as part of the
comment that is placed in the public docket and made available on the
Internet. If you submit an electronic comment, EPA recommends that you
include your name and other contact information in the body of your
comment and with any disk or CD-ROM you submit. If EPA cannot read your
comment due to technical difficulties and cannot contact you for
clarification, EPA may not be able to consider your comment. Electronic
files should avoid the use of special characters, any form of
encryption, and be free of any defects or viruses. For additional
information about EPA's public docket visit the EPA Docket Center
homepage at https://www.epa.gov/epahome/dockets.htm.
Docket: All documents in the docket are listed in the
www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, will be publicly available only in hard copy.
Publicly available docket materials are available either electronically
in www.regulations.gov or in hard copy at the Air and Radiation Docket,
EPA/DC, EPA West, Room 3334, 1301 Constitution Ave. NW., Washington,
DC. The Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday
through Friday, excluding legal holidays. The telephone number for the
Public Reading Room is (202) 566-1744, and the telephone number for the
Air and Radiation Docket is (202) 566-1742).
FOR FURTHER INFORMATION CONTACT: For further information about this
proposed rule, contact Jeremy Arling by telephone at (202) 343-9055, or
by email at arling.jeremy@epa.gov or by mail at U.S. Environmental
Protection Agency, Stratospheric Protection Division, Stratospheric
Program Implementation Branch (6205J), 1200 Pennsylvania Avenue NW.,
Washington, DC 20460. You may also visit the methyl bromide section of
the Ozone Depletion Web site of EPA's Stratospheric Protection Division
at www.epa.gov/ozone/mbr for further information about the methyl
bromide critical use exemption, other Stratospheric Ozone Protection
regulations, the science of ozone layer depletion, and related topics.
SUPPLEMENTARY INFORMATION: This proposed rule concerns Clean Air Act
(CAA) restrictions on the consumption, production, and use of methyl
bromide (a Class I, Group VI controlled substance) for critical uses
during calendar year 2013. Under the Clean Air Act, methyl bromide
consumption (consumption is defined under section 601 of the CAA as
production plus imports minus exports) and production were phased out
on January 1, 2005, apart from allowable exemptions, such as the
critical use and the quarantine and preshipment (QPS) exemptions. With
this action, EPA is proposing and seeking comment on the uses that will
qualify for the 2013 critical use exemption as well as specific amounts
of methyl bromide that may be produced and imported, or sold from pre-
phaseout inventory (also referred to as ``stocks'' or ``inventory'')
for proposed critical uses in 2013.
Table of Contents
I. General Information
A. Regulated Entities
B. What should I consider when preparing my comments?
II. What is methyl bromide?
III. What is the background to the phaseout regulations for ozone-
depleting substances?
IV. What is the legal authority for exempting the production and
import of methyl bromide for critical uses authorized by the parties
to the Montreal Protocol?
V. What is the critical use exemption process?
A. Background of the Process
B. How does this proposed rule relate to previous critical use
exemption rules?
C. Stocks of Methyl Bromide
D. Proposed Critical Uses
E. Proposed Critical Use Amounts
[[Page 74436]]
1. Approach for Determining Critical Stock Allowances
2. Approach for Determining New Production and Import Allowances
F. The Criteria in Decisions IX/6 and Ex. I/4
G. Emissions Minimization
VI. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review and
Executive Order 13563: Improving Regulation and Regulatory Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
G. Executive Order 13045: Protection of Children From
Environmental Health and Safety Risks
H. Executive Order 13211: Actions That Significantly Affect
Energy Supply, Distribution, or Use
I. National Technology Transfer and Advancement Act
J. Executive Order 12898: Federal Actions to Address
Environmental Justice in Minority Populations and Low-Income
Populations
I. General Information
A. Regulated Entities
Entities potentially regulated by this proposed action are those
associated with the production, import, export, sale, application, and
use of methyl bromide covered by an approved critical use exemption.
Potentially regulated categories and entities include producers,
importers, and exporters of methyl bromide; applicators and
distributors of methyl bromide; and users of methyl bromide that
applied for the 2013 critical use exemption including growers of
vegetable crops, fruits and nursery stock, and owners of stored food
commodities and structures such as grain mills and processors. This
list is not intended to be exhaustive, but rather to provide a guide
for readers regarding entities likely to be regulated by this proposed
action. To determine whether your facility, company, business, or
organization could be regulated by this proposed action, you should
carefully examine the regulations promulgated at 40 CFR part 82,
subpart A. If you have questions regarding the applicability of this
action to a particular entity, consult the person listed in the
preceding section.
B. What should I consider when preparing my comments?
1. Confidential Business Information. Do not submit confidential
business information (CBI) to EPA through www.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 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. Information so marked will not be disclosed except
in accordance with procedures set forth in 40 CFR part 2. 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.
2. Tips for Preparing Your Comments. When submitting comments,
remember to:
Identify the rulemaking by docket number and other
identifying information (subject heading, Federal Register date, and
page number).
Follow directions--The agency may ask you to respond to
specific questions or organize comments by referencing a Code of
Federal Regulations (CFR) part or section number.
Explain why you agree or disagree; suggest alternatives
and substitute language for your requested changes.
Describe any assumptions and provide any technical
information and/or data that you used.
If you estimate potential costs or burdens, explain how
you arrived at your estimate in sufficient detail to allow for it to be
reproduced.
Provide specific examples to illustrate your concerns, and
suggest alternatives.
Explain your views as clearly as possible, avoiding the
use of profanity or personal threats.
Make sure to submit your comments by the comment period
deadline identified.
II. What is methyl bromide?
Methyl bromide is an odorless, colorless, toxic gas which is used
as a broad-spectrum pesticide and is controlled under the CAA as a
Class I ozone-depleting substance (ODS). Methyl bromide was once widely
used as a fumigant to control a variety of pests such as insects,
weeds, rodents, pathogens, and nematodes. Information on methyl bromide
can be found at https://www.epa.gov/ozone/mbr.
Methyl bromide is also regulated by EPA under the Federal
Insecticide, Fungicide, and Rodenticide Act (FIFRA) and other statutes
and regulatory authority, as well as by States under their own statutes
and regulatory authority. Under FIFRA, methyl bromide is a restricted
use pesticide. Restricted use pesticides are subject to Federal and
State requirements governing their sale, distribution, and use. Nothing
in this proposed rule implementing the Clean Air Act is intended to
derogate from provisions in any other Federal, State, or local laws or
regulations governing actions including, but not limited to, the sale,
distribution, transfer, and use of methyl bromide. Entities affected by
this proposal must continue to comply with FIFRA and other pertinent
statutory and regulatory requirements for pesticides (including, but
not limited to, requirements pertaining to restricted use pesticides)
when importing, exporting, acquiring, selling, distributing,
transferring, or using methyl bromide for critical uses. The provisions
in this proposed action are intended only to implement the CAA
restrictions on the production, consumption, and use of methyl bromide
for critical uses exempted from the phaseout of methyl bromide.
III. What is the background to the phaseout regulations for ozone-
depleting substances?
The regulatory requirements of the stratospheric ozone protection
program that limit production and consumption of ozone-depleting
substances are in 40 CFR part 82, subpart A. The regulatory program was
originally published in the Federal Register on August 12, 1988 (53 FR
30566), in response to the 1987 signing and subsequent ratification of
the Montreal Protocol on Substances that Deplete the Ozone Layer
(Montreal Protocol). The Montreal Protocol is the international
agreement aimed at reducing and eliminating the production and
consumption of stratospheric ozone-depleting substances. The United
States was one of the original signatories to the 1987 Montreal
Protocol and the United States ratified the Protocol on April 12, 1988.
Congress then enacted, and President George H.W. Bush signed into law,
the Clean Air Act Amendments of 1990 (CAAA of 1990) which included
Title VI on Stratospheric Ozone Protection, codified as 42 U.S.C.
Chapter 85, Subchapter VI, to ensure that the United States could
satisfy its obligations under the Protocol. EPA issued regulations to
implement this legislation and has since amended the regulations as
needed.
Methyl bromide was added to the Protocol as an ozone-depleting
substance in 1992 through the Copenhagen Amendment to the Protocol. The
Parties to the Montreal Protocol (Parties) agreed that each developed
country's level of methyl bromide production and consumption in 1991
should be the baseline for establishing a freeze on the level of
[[Page 74437]]
methyl bromide production and consumption for developed countries. EPA
published a final rule in the Federal Register on December 10, 1993 (58
FR 65018), listing methyl bromide as a Class I, Group VI controlled
substance. This rule froze U.S. production and consumption at the 1991
baseline level of 25,528,270 kilograms, and set forth the percentage of
baseline allowances for methyl bromide granted to companies in each
control period (each calendar year) until 2001, when the complete
phaseout would occur. This phaseout date was established in response to
a petition filed in 1991 under sections 602(c)(3) and 606(b) of the
CAAA of 1990, requesting that EPA list methyl bromide as a Class I
substance and phase out its production and consumption. This date was
consistent with section 602(d) of the CAAA of 1990, which, for newly
listed Class I ozone-depleting substances provides that ``no extension
[of the phaseout schedule in section 604] under this subsection may
extend the date for termination of production of any class I substance
to a date more than 7 years after January 1 of the year after the year
in which the substance is added to the list of class I substances.''
At the Seventh Meeting of the Parties (MOP) in 1995, the Parties
made adjustments to the methyl bromide control measures and agreed to
reduction steps and a 2010 phaseout date for developed countries with
exemptions permitted for critical uses. At that time, the United States
continued to have a 2001 phaseout date in accordance with section
602(d) of the CAAA of 1990. At the Ninth MOP in 1997, the Parties
agreed to further adjustments to the phaseout schedule for methyl
bromide in developed countries, with reduction steps leading to a 2005
phaseout. The Parties also established a phaseout date of 2015 for
Article 5 countries.
IV. What is the legal authority for exempting the production and import
of methyl bromide for critical uses authorized by the parties to the
Montreal Protocol?
In October 1998, the U.S. Congress amended the Clean Air Act (CAA)
to prohibit the termination of production of methyl bromide prior to
January 1, 2005, to require EPA to bring the U.S. phaseout of methyl
bromide in line with the schedule specified under the Protocol, and to
authorize EPA to provide certain exemptions. These amendments were
contained in Section 764 of the 1999 Omnibus Consolidated and Emergency
Supplemental Appropriations Act (Pub. L. 105-277, October 21, 1998) and
were codified in section 604 of the CAA, 42 U.S.C. 7671c. The amendment
that specifically addresses the critical use exemption appears at
section 604(d)(6), 42 U.S.C. 7671c(d)(6). EPA revised the phaseout
schedule for methyl bromide production and consumption in a direct
final rulemaking on November 28, 2000 (65 FR 70795), which allowed for
the reduction in methyl bromide consumption specified under the
Protocol and extended the phaseout to 2005 while creating a placeholder
for critical use exemptions. EPA again amended the regulations to allow
for an exemption for quarantine and preshipment (QPS) purposes through
an interim final rule on July 19, 2001 (66 FR 37751), and a final rule
on January 2, 2003 (68 FR 238).
On December 23, 2004 (69 FR 76982), EPA published a final rule (the
``Framework Rule'') that established the framework for the critical use
exemption, set forth a list of approved critical uses for 2005, and
specified the amount of methyl bromide that could be supplied in 2005
from stocks and new production or import to meet the needs of approved
critical uses. EPA subsequently published rules applying the critical
use exemption framework for each of the annual control periods from
2006 to 2012. Under authority of section 604(d)(6) of the CAA, today's
action proposes the uses that will qualify as approved critical uses in
2013 and the amount of methyl bromide that may be produced, imported,
or supplied from inventory to satisfy those uses.
This proposed action on critical uses for 2013 reflects Decision
XXIII/4, taken at the Twenty-Third Meeting of the Parties in November
2011. In accordance with Article 2H(5), the Parties have issued several
Decisions pertaining to the critical use exemption. These include
Decisions IX/6 and Ex. I/4, which set forth criteria for reviewing
proposed critical uses. The status of Decisions is addressed in NRDC v.
EPA, (464 F.3d 1, DC Cir. 2006) and in EPA's ``Supplemental Brief for
the Respondent,'' filed in NRDC v. EPA and available in the docket for
this action. In this proposed rule on critical uses for 2013, EPA is
honoring commitments made by the United States in the Montreal Protocol
context.
V. What is the critical use exemption process?
A. Background of the Process
The critical use exemption is designed to permit the production and
import of methyl bromide for uses that do not have technically and
economically feasible alternatives that are acceptable from the
standpoint of environment and health and for which the lack of methyl
bromide would result in significant market disruption (40 CFR 82.3).
Article 2H of the Montreal Protocol established the critical use
exemption provision. At the Ninth Meeting of the Parties (1997), the
Parties established the criteria for an exemption in Decision IX/6. In
that Decision, the Parties agreed that ``a use of methyl bromide should
qualify as `critical' only if the nominating Party determines that: (i)
The specific use is critical because the lack of availability of methyl
bromide for that use would result in a significant market disruption;
and (ii) there are no technically and economically feasible
alternatives or substitutes available to the user that are acceptable
from the standpoint of environment and public health and are suitable
to the crops and circumstances of the nomination.'' These criteria are
reflected in EPA's definition of ``critical use'' at 40 CFR 82.3. In
addition, the Parties decided that production and consumption, if any,
of methyl bromide for critical uses should be permitted only if a
variety of conditions have been met, including that all technically and
economically feasible steps have been taken to minimize the critical
use and any associated emission of methyl bromide, that research
programs are in place to develop and deploy alternatives and
substitutes, and that methyl bromide is not available in sufficient
quantity and quality from existing stocks of banked or recycled methyl
bromide.
In response to EPA's request for critical use exemption
applications published in the Federal Register on July 15, 2010 (75 FR
41177), applicants provided data on the technical and economic
feasibility of using alternatives to methyl bromide. Applicants also
submitted data on their use of methyl bromide, ongoing research
programs into the use of alternatives to methyl bromide in their
sector, and efforts to minimize use and emissions of methyl bromide.
EPA reviews the data submitted by applicants, as well as data from
governmental and academic sources, to establish whether there are
technically and economically feasible alternatives available for a
particular use of methyl bromide, and whether there would be a
significant market disruption if no exemption were available. In
addition, an interagency workgroup reviews other parameters of the
exemption applications such as dosage and emissions minimization
techniques and applicants' research or transition plans.
[[Page 74438]]
This assessment process culminates in the development of a document
referred to as the U.S. critical use nomination (CUN). Since 2003, the
U.S. Department of State has submitted a CUN annually to the United
Nations Environment Programme (UNEP) Ozone Secretariat. The Methyl
Bromide Technical Options Committee (MBTOC) and the Technology and
Economic Assessment Panel (TEAP), which are advisory bodies to Parties
to the Montreal Protocol, review each Party's CUN and make
recommendations to the Parties on the nominations. The Parties then
take Decisions to authorize critical use exemptions for particular
Parties, including how much methyl bromide may be supplied for the
exempted critical uses. As required in section 604(d)(6) of the CAA,
for each exemption period, EPA consults with the United States
Department of Agriculture (USDA) and other departments and institutions
of the Federal government that have regulatory authority related to
methyl bromide, and provides an opportunity for public comment on the
amounts and specific uses of methyl bromide that the agency is
proposing to exempt.
On February 4, 2011, the U.S. Government (USG) submitted the ninth
Nomination for a Critical Use Exemption for Methyl Bromide for the
United States of America to the Ozone Secretariat of UNEP. This
nomination contained the request for 2013 critical uses. In February
2011, MBTOC sent questions to the USG concerning technical and economic
issues in the 2013 nomination. The USG transmitted responses to MBTOC
in February, 2011. These documents, together with reports by the
advisory bodies noted above, are in the public docket for this
rulemaking. The proposed critical uses and amounts reflect the analysis
contained in those documents.
B. How does this proposed rule relate to previous critical use
exemption rules?
The December 23, 2004, Framework Rule (69 FR 76982) established the
framework for the critical use exemption program in the United States,
including definitions, prohibitions, trading provisions, and
recordkeeping and reporting obligations. The preamble to the Framework
Rule included EPA's determinations on key issues for the critical use
exemption program.
Since publishing the Framework Rule, EPA has annually promulgated
regulations to exempt specific quantities of production and import of
methyl bromide, to determine the amounts that may be supplied from pre-
phaseout inventory, and to indicate which uses meet the criteria for
the exemption program for that year. See 71 FR 5985 (February 6, 2006),
71 FR 75386 (December 14, 2006), 72 FR 74118 (December 28, 2007), 74 FR
19878 (April 30, 2009), 75 FR 23167 (May 3, 2010), 76 FR 60737
(September 30, 2011), and 77 FR 29218 (May 17, 2012).
Today's action proposes to amend the regulatory framework to
determine the amounts of Critical Use Allowances (CUAs) and Critical
Stock Allowances (CSAs) to be allocated for critical uses in 2013. A
CUA is the privilege granted through 40 CFR part 82 to produce or
import 1 kg of methyl bromide for an approved critical use during the
specified control period. These allowances expire at the end of the
control period and, as explained in the Framework Rule, are not
bankable from one year to the next. The proposed CUA allocation is
subject to the trading provisions at 40 CFR 82.12, which are discussed
in section V.G. of the preamble to the Framework Rule (69 FR 76982).
A CSA is the right granted through 40 CFR part 82 to sell 1 kg of
methyl bromide from inventory produced or imported prior to the January
1, 2005, phaseout date for an approved critical use during the
specified control period. The Framework Rule established provisions
governing the sale of pre-phaseout inventories for critical uses,
including the concept of CSAs and a prohibition on the sale of pre-
phaseout inventories for critical uses in excess of the amount of CSAs
held by the seller. It also established trading provisions that allow
CUAs to be converted into CSAs.
C. Stocks of Methyl Bromide
An approved critical user may purchase methyl bromide produced or
imported with CUAs, as well as limited inventories of pre-phaseout
methyl bromide, the combination of which constitute the supply of
``critical use methyl bromide'' intended to meet the needs of approved
critical uses. EPA considers all pre-phaseout inventory to be suitable
for both pre-plant and post harvest uses. The aggregate amount of pre-
phaseout methyl bromide reported as being in inventory at the beginning
of 2012 is 1,248,876 kg. This amount does not include critical use
methyl bromide that was produced after January 1, 2005, and carried
over into subsequent years. Nor does it include methyl bromide produced
(1) Under the quarantine and preshipment (QPS) exemption, (2) with
Article 5 allowances to meet the basic domestic needs of Article 5
countries, or (3) for feedstock or transformation purposes. As in prior
years, the Agency will continue to closely monitor CUA and CSA data. As
stated in the final 2006 CUE Rule, if an inventory shortage occurs, EPA
may consider various options including authorizing the conversion of a
limited number of CSAs to CUAs through a rulemaking, bearing in mind
the upper limit on U.S. production/import for critical uses. In
sections V.D. and V.G. of this preamble, EPA seeks comment on the
amount of critical use methyl bromide to come from inventory compared
to new production and import.
As explained in the 2008 CUE Rule, the agency intends to continue
releasing aggregate methyl bromide inventory information reported to
the agency under the reporting requirements at 40 CFR 82.13 at the end
of each control period. EPA notes that if the number of competitors in
the industry were to decline appreciably, EPA would revisit the
question of whether the aggregate is entitled to treatment as
confidential information and whether to release the aggregate without
notice. EPA is not proposing to change the treatment of submitted
information but welcomes information concerning the composition of the
industry in this regard. The aggregate information for 2003 through
2012 is available in the docket for this rulemaking.
D. Proposed Critical Uses
In Decision XXIII/4, taken in November 2011, the Parties to the
Protocol agreed ``to permit, for the agreed critical-use categories for
2013 set forth in table A of the annex to the present decision for each
party, subject to the conditions set forth in the present decision and
in decision Ex.I/4 to the extent that those conditions are applicable,
the levels of production and consumption for 2013 set forth in table B
of the annex to the present decision which are necessary to satisfy
critical uses * * * ''
The following uses are those set forth in table A of the annex to
Decision XXIII/4 for the United States:
Commodities
Mills and food processing structures
Dried cured pork
Cucurbits
Eggplant--field
Nursery stock--fruit, nuts, flowers
Orchard replants
Ornamentals
Peppers--field
Strawberry--field
Strawberry runners
Tomatoes--field
EPA is seeking comment on the technical analysis contained in the
U.S. nomination (available for public review in the docket to this
rulemaking), and
[[Page 74439]]
seeks information regarding any changes to the registration (including
cancellation or new registrations), use, or efficacy of alternatives
that have transpired after the 2013 U.S. CUN was forwarded. EPA
recognizes that as the market for alternatives evolves, the thresholds
for what constitutes ``significant market disruption'' or ``technical
and economic feasibility'' may change. Comments on technical data
contained in the CUN, or new information, could potentially alter the
agency's analysis on the uses and amounts of methyl bromide qualifying
for the critical use exemption. The agency may, in response to new
information, reduce the proposed quantities of critical use methyl
bromide, or decide not to approve uses authorized by the Parties.
However, the agency will not increase the quantities or add new uses in
the final rule beyond those authorized by the Parties.
EPA is also proposing to modify the table in 40 CFR part 82,
subpart A, appendix L to reflect the agreed critical use categories
identified in Decision XXIII/4. The agency is amending the table of
critical uses and critical users based in part on the technical
analysis contained in the 2013 U.S. nomination that assesses data
submitted by applicants to the CUE program. First, EPA is proposing to
remove two users who did not submit applications and therefore were not
included in the U.S. nomination. These users are California rose
nursery growers and Maryland tomato growers.
Second, EPA is proposing to remove the National Pest Management
Association (NPMA) food processing use from the list for 2013. The NPMA
did not initially apply to be a critical user in 2013 and the Parties
have not authorized a critical use for this purpose for 2013. Members
of the NPMA have worked to transition from methyl bromide to
alternative practices and alternative fumigants like sulfuryl fluoride.
In January 2004, EPA registered the first food uses of sulfuryl
fluoride for control of insect pests in grain processing facilities and
in harvested and processed food commodities such as cereal grains,
dried fruits, and tree nuts. In July 2005, EPA approved sulfuryl
fluoride for treatment of additional harvested and processed food
commodities such as coffee and cocoa beans, and for fumigation of food
handling and processing facilities.
On January 19, 2011, EPA proposed to revoke the residue limits on
food, known as tolerances, for fluoride on the food commodities
approved for treatment with sulfuryl fluoride (76 FR 3422). In response
to this proposal, the NPMA submitted a supplemental request for 2013
during the open period for 2014 applications. The USG did not include
NPMA's supplemental request in the 2014 nomination submitted to UNEP on
January 31, 2012, because EPA has only proposed to revoke the
tolerances for sulfuryl fluoride and has not taken action in any final
rule. U.S. critical use nominations have been based on final decisions
about alternatives. Additionally, the proposed tolerance revocation
rule includes a staggered implementation scheme, making it unlikely
that any specific revocation will be effective in 2013. Therefore, EPA
is not proposing NPMA as a critical use in 2013.
Third, EPA is proposing to remove sectors or users that applied for
a critical use in 2013 but that the United States did not nominate for
2013. EPA conducted a thorough technical assessment of each application
and considered the effects that the loss of methyl bromide would have
for each agricultural sector, and whether significant market disruption
would occur as a result. As a result of this technical review, the U.S.
Government did not find that certain sectors or users met the critical
use criteria in Decision IX/6 and they were therefore not included in
the 2013 Critical Use Nomination. EPA notified these sectors of their
status in July 2011. These sectors are: members of the Southeastern
Cucurbit Consortium and cucurbit growers in Maryland and Delaware;
growers in the forest nursery sector (Southern Forest Nursery
Management Cooperative, Northeastern Forest and Conservation Nursery
Association, and Michigan seedling growers); members of the
Southeastern Pepper Consortium; members of the Southeastern Strawberry
Consortium and Florida strawberry growers; California sweet potato slip
growers; members of the Southeastern Tomato Consortium and Virginia
tomato growers. For each of these uses, EPA found that there are
technically and economically feasible alternatives to methyl bromide.
Finally, EPA is proposing to limit the CUE for cucurbit, eggplant,
pepper, and tomato sectors in Georgia to small growers. The EPA review
of the available information for Georgia indicates that farmers growing
fewer than 10 acres of these crops need an additional year to
successfully transition to the alternatives. These small growers do not
have as much experience with the alternatives and need to convert their
equipment to the University of Georgia (UGA) ``3-Way'' mixture (a
combination of 1,3-dichloropropene, chloropicrin, and metam). The EPA
conducted an economic assessment of small growers' ability to convert
their equipment (see revised nomination, dated July 15, in the docket).
The assessment demonstrates that despite the UGA 3-Way mixture being
more affordable than methyl bromide plus chloropicrin on a per acre
basis, retrofitting farm equipment to use the UGA 3-Way mixture at a
cost of $3,450 is not affordable for growers under four acres,
amortized over 10 years at 7% interest (7% is a home equity loan rate
for this region at the time the nomination was submitted; interest on
agricultural loans could be lower). However, due to variations in
impacts for individual growers and uncertainties in the assumptions
used in the economic analysis, farms smaller than 10 acres are
reasonably expected to incur negative impacts from having to covert to
the UGA 3-Way mixture. Therefore, EPA is proposing to limit the Georgia
cucurbit, eggplant, pepper, and tomato critical uses to small growers,
which EPA is proposing to define as growers growing fewer than 10
acres. EPA seeks comment on these proposed changes to Appendix L.
EPA is not proposing other changes to the table but is repeating
the following clarifications made in previous years for ease of
reference. The ``local township limits prohibiting 1,3-
dichloropropene'' are prohibitions on the use of 1,3-dichloropropene
products in cases where local township limits on use of this
alternative have been reached. In addition, ``pet food'' under
subsection B of Food Processing refers to food for domesticated dogs
and cats. Finally, ``rapid fumigation'' for commodities is when a buyer
provides short (two working days or fewer) notification for a purchase
or there is a short period after harvest in which to fumigate and there
is limited silo availability for using alternatives.
E. Proposed Critical Use Amounts
Table A of the annex to Decision XXIII/4 lists critical uses and
amounts agreed to by the Parties to the Montreal Protocol. When added
together, the total authorized critical use for 2013 for the United
States is 562,326 kilograms (kg), which is equivalent to 2.2% of the
U.S. 1991 methyl bromide consumption baseline of 25,528,270 kg. The
maximum amount of new production and import for U.S. critical uses,
specified in Table B of Decision XXIII/4, is 562,326 kg, minus
available stocks. In previous years, the maximum amount of new
production has been less than the total authorization, with the
[[Page 74440]]
difference representing the minimum amount that the Parties expect to
be used from pre-phaseout inventory. For 2013 the Parties indicated
that the United States should use ``available stocks,'' but unlike
previous years, Decision XXIII/4 did not indicate a minimum amount
expected to be taken from stocks. Consistent with EPA's past practice,
and our commitments to the Parties, EPA is considering the level of
``available stocks'' that may be allocated in this rulemaking. However,
EPA is seeking comment on changing the approach for determining the
availability of stocks in this rule.
As established in earlier rulemakings, EPA views the determination
of the total allocation, up to the amount authorized by the Parties, as
an appropriate exercise of discretion. The Agency may decide to
allocate less than the full amount authorized by the Parties, and in
past CUE rules EPA has made reductions to the total allocation after
considering several factors, including new data on alternatives, such
as the registration of a new alternative not considered when the CUN
was submitted to UNEP, and carryover from prior years. For 2013, EPA
does not have new data regarding the uptake of new alternatives.
However, iodomethane, an alternative that was available when the CUN
was submitted, is no longer available. EPA believes this is an
important factor that should be considered in determining the total
amount of the allocation; however, because of the schedule for
consideration under the Montreal Protocol, the timing of withdrawal
complicates any recognition by the Parties of this development for
2013. In addition, as detailed below, carryover for 2012 is zero and
EPA is not proposing reductions on that basis. EPA is therefore
proposing to allocate 562,326 kg, the full amount authorized by the
Parties, in particular due to the loss of iodomethane. EPA welcomes
comment on the proposed levels of exempted new production and import
for critical uses and the amount of material that may be sold from pre-
phaseout inventory for critical uses.
1. Approach for Determining Critical Stock Allowances
EPA is proposing a new approach for determining the amount of CSAs
and CUAs to allocate. EPA is proposing to calculate ``available
stocks'' as a percentage of the existing inventory, as was reported to
EPA on January 1, 2012. Under this approach, EPA is soliciting comment
on two different amounts of ``available stocks'', and thus two
different possible allocations of CSAs. EPA is also soliciting comment
on a separate approach that would continue to use the framework
methodology to calculate the amount of ``available stocks'' by
estimating drawdown during 2012 and providing for a supply chain factor
for 2013. As noted above, EPA is proposing to not reduce the critical
use authorization of the Parties, and thus is proposing that any
authorized amount not allocated as CSAs be allocated as new production
and import allowances.
In past CUE allocation rules, EPA allocated CSAs in amounts that
represented not only the difference between the total authorized CUE
amount and the amount of authorized new production and import but also
an additional amount to reflect available stocks. After determining the
CSA amount, EPA determined the portion of CUE methyl bromide to come
from new production and import such that the total amount of methyl
bromide exempted for critical uses did not exceed the total amount
authorized by the Parties for that year.
EPA views the decision whether to include these additional amounts
in the calculation of the year's overall CSA level as an appropriate
exercise of discretion. The Agency is not required to allocate the full
amount of authorized new production and consumption. The Parties only
agree to ``permit'' a particular level of production and consumption;
they do not--and cannot--mandate that the United States authorize this
level of production and consumption domestically. Nor does the CAA
require EPA to allow the full amount permitted by the Parties. Section
604(d)(6) of the CAA does not require EPA to exempt any amount of
production and consumption from the phaseout, but instead specifies
that the Agency ``may'' create an exemption for critical uses,
providing EPA with substantial discretion.
When determining the CSA amounts, EPA considers what portion of
existing stocks would be ``available'' for critical uses during that
control period. The Parties to the Protocol recognized in their
Decisions that the level of existing stocks may differ from the level
of available stocks. Decision XXIII/4 states that ``production and
consumption of methyl bromide for critical uses should be permitted
only if methyl bromide is not available in sufficient quantity and
quality from existing stocks * * *.'' In addition, earlier Decisions
refer to the use of ``quantities of methyl bromide from stocks that the
Party has recognized to be available.'' Thus, it is clear that
individual Parties have the ability to determine their level of
available stocks. Decision XXIII/4 further reinforces this concept by
including the phrase ``minus available stocks'' as a footnote to the
United States' authorized level of production and consumption in Table
B. Section 604(d)(6) of the CAA does not require EPA to adjust the
amount of new production and import to reflect the availability of
stocks; however, as explained in previous rulemakings, making such an
adjustment is a reasonable exercise of EPA's discretion under this
provision.
In recent CUE rules, EPA has calculated the amount of ``available
stocks'' using a formula adopted in the 2008 CUE rule: ASCP
= ESPP-DPP-SCFCP, where
ASCP would be the available stocks on the first day of the
control period; ESPP would be the existing pre-phaseout
stocks of methyl bromide held in the United States by producers,
importers, and distributors on the first day of the prior control
period; DPP would be the estimated drawdown of existing
stocks during the prior control period; and SCFCP would be
the supply chain factor for the control period. In the section below,
EPA is taking comment on using this approach, and is alternatively
proposing a new approach, for determining the amount of available
stocks.
Option 1: Percentage of Existing Inventory
For 2013, EPA is proposing a new approach that would allocate
critical stock allowances in an amount equal to a percentage of the
existing inventory. Under this approach, EPA proposes to calculate
``available stocks'' as a percentage of the existing inventory, as was
reported to EPA on January 1, 2012. EPA is considering alternate
approaches for allocating critical stock allowances because the old
approach, discussed as option 2 below, may be increasingly inaccurate
as the amount of inventory declines, overly complex, and contributing
to delay in issuing the final critical use exemption. Furthermore, EPA
believes that efforts to in estimate available inventory may be further
complicated for 2013 by the recent withdrawal of iodomethane from the
market.
In the 2012 Final Rule, EPA recognized ``that its estimates [of
available stocks] have become increasingly inexact in characterizing
actual drawdown of pre-phaseout inventory, as the amounts in inventory
have declined over time. EPA intends to consider the adequacy of using
this formula to assess `available stocks' in a future action.''
Initially, the drawdown estimate was a simple linear model based on
past years' rates. EPA modified
[[Page 74441]]
the approach when it became apparent that the inventory drawdown was
decreasing exponentially rather than linearly. EPA noted in the 2009
CUE Rule that the rate of drawdown was based mostly on the business
decisions of the companies that hold pre-phaseout inventory, and
included aspects that are difficult for EPA to know or quantify, such
as honoring long-term relationships with non-CUE customers or holding
inventory in response to price fluctuations. To refine the analysis in
subsequent rules EPA separately analyzed the use of inventory on
critical uses, for which there are a set number of allowances, and non-
critical uses, for which there are not. This approach is discussed in
more detail below.
Despite increased specificity, precise estimates still proved
elusive. In successive years, EPA substantially overestimated inventory
drawdown. Most recently, in the 2012 Rule, EPA estimated a drawdown of
1,110,633 kg, when the actual drawdown was half that amount, or 556,794
kg. The results of the methodology using the updated data were
sufficiently different that EPA considered providing additional notice
and the opportunity to comment to incorporate them into the final
allocation rule. EPA is concerned that as the total amount of both the
U.S. authorization and the pre-phaseout stocks become smaller, efforts
to perfect EPA estimates in this area will delay needed rulemaking.
Moreover, EPA believes that the fact that its projections
consistently over-estimate the amount of inventory that will be drawn
down is evidence that EPA has been substantially over-estimating the
availability of pre-phaseout stocks. EPA has received comments in past
rulemakings that existing inventory was not actually available to users
because of reductions in the number of distributors, and decisions by
distributors not to sell inventory. While EPA believes it is
appropriate to rely on market flexibility and efficiency to distribute
existing stocks of inventory, EPA recognizes that the data appear to
show that inventory is less ``available'' than was estimated under
EPA's prior approach.
EPA believes problems with the existing formula may also become
worse due to a recent change in the geographic distribution of critical
users. In the past, EPA has considered all pre-phaseout inventory to be
available to all users, regardless of location. This assumption, as
discussed in the 2009 CUE rule (74 FR 19887, April 30, 2009), was based
on the fact that inventory is held in California and the Southeast, as
well as other locations around the country. While the geographic
distribution of inventory generally remains the same, the authorized
critical uses have shifted to California over the last two years. In
the 2011 control period, 49% of the total authorization was for pre-
plant uses in California and 38% was for pre-plant uses in the
Southeast. In 2013, this ratio will be 91% and 4% respectively.\1\
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\1\ EPA treats company-specific methyl bromide inventory
information as confidential and believes that disaggregating the
inventory data by geographic area could potentially reveal CBI. EPA
solicits comment on this issue but is not proposing at this time to
release data showing how much inventory is located in or near
California. However, even in the absence of specific inventory data
broken down by region, EPA believes that the fact that over 90% of
critical use is in California is relevant to judging the
availability of existing stocks.
---------------------------------------------------------------------------
EPA believes that inventory held in the Southeast may not be
equally available to critical users in California. Stakeholders have
told EPA that distributors do not ship pre-phaseout inventory to buyers
across the country. Unlike newly produced or imported material which
enters nationwide distribution networks, inventory is mostly held by
regional distributors. In addition, those distributors typically sell
both the gas and the application services together. Distributors would
therefore incur additional expense to ship material without being able
to charge for performing the application. EPA specifically encourages
comment on the question of whether inventory held in one part of the
country has been, or can be, transported to critical uses in another
part of the country.
Another reason EPA is proposing to allocate critical stock
allowances equal to a percentage of the existing inventory is that EPA
believes this method will be easier to calculate and will help
streamline the issuance of the CUE allocation rule. EPA has received
comment in the past few CUE Rules that the agency should find ways to
issue the allocation rulemakings before the start of the control
period. In the 2012 CUE final rule, EPA stated that the agency ``will
consider means of streamlining the Critical Use Exemption rulemaking in
the future so that the rule can be issued prior to the start of the
control period.'' Absent that, EPA will seek to issue a final rule as
soon into the control period as possible. EPA is concerned that efforts
to correct estimates and incorporate the most recent data into the
calculation of the supply chain factor and the rest of the formula will
further delay future CUE rules. EPA recognized in the 2012 Rule that
``the time-sensitive need for a CUE authorization for the current
calendar year and concluded that re-opening the allocation for comment
is not warranted.'' EPA believes that its prior formula may have
attempted to achieve greater precision than was possible or needed,
especially in light of the continued reduction in both inventory and
annual authorizations for critical uses. Thus, EPA is considering an
alternate approach, which provides a greater likelihood of expediting
the rulemaking process. EPA will continue to consider other possible
means of streamlining the CUE rulemaking process in the future.
As part of this approach, EPA would end its use of the supply chain
factor (SCF).\2\ Because this approach does not use the available
stocks calculation developed in the 2008 CUE Rule to determine the
amount of available stocks for use by critical users in 2013,
calculation of the SCF is unnecessary. EPA notes that the entire
critical use exemption authorized by the Parties for 2013 is 562 MT,
which is substantially less than the existing inventory. EPA believes
that, although portions of the existing inventory may not practically
be available under usual circumstances (e.g., because it may be located
in the Southeast and not California), users may be able to access
greater amounts of inventory in the event of extraordinary
circumstances such as a catastrophic domestic production failure.
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\2\ The purpose, and calculation, of the supply chain factor is
discussed in greater detail below, and in prior CUE notices.
---------------------------------------------------------------------------
In addition to soliciting comment on this approach to calculating
CSAs, EPA is also soliciting comment on the specific amount of
inventory to be allocated. EPA is proposing to allocate CSAs equal to
5% of the January 1, 2012, reported inventory. Alternatively, EPA is
also taking comment on not allocating any CSAs for 2013 under this
approach in light of the effect that the withdrawal of iodomethane may
have on the demand for inventory. The two options are discussed below.
EPA is proposing to allocate CSAs equal to 5% of the January 1,
2012, reported inventory. The inventory at that date was 1,248,876 kg.
Therefore, under this approach, EPA would allocate 62,444 kg of
critical stock allowances for 2013. Since 2006, the amount of prior
year inventory used through the expenditure of CSAs has ranged from 8%
to 26%. EPA believes that it would be appropriate to select a
percentage that is below the historic range for several reasons. First,
EPA wishes to ensure that the amount allocated for 2013 will be
available to critical users in that year. As discussed above, the
availability of existing inventory is becoming increasingly difficult
to estimate as the amount
[[Page 74442]]
declines. Although EPA is proposing to consider historic patterns of
availability in considering how many CSAs to allocate, the fact that
stocks in the Southeast may be unavailable as a practical matter for
growers in California, while critical uses have recently become highly
concentrated in California, suggests that, even under this approach, a
conservative approach to estimating availability of inventory is
warranted. As noted above, this issue is particularly important for
2013 because the unexpected withdrawal of iodomethane.
EPA believes it is reasonable to assume that 5% of existing
inventory on January 1, 2012, could be available for critical users in
2013. Historically, the drawdown of inventory for all uses has never
exceeded 42% of the prior year's inventory. Drawdown would have to be
over twice that rate in 2012 for there to be less inventory in 2013
than the amount of the proposed CSA. Rather, EPA anticipates that the
constraints on drawdown discussed in prior rules (e.g., critical uses
capped by allocation amounts, revised labeling removing uses, increased
value of the material as supply decreases) will continue to limit the
drawdown in 2012. At the same time, expenditure of CSAs have never
amounted to less than 8% of inventory, and even if inventory was
purchased for critical uses at only half that rate, it would still
amount to 4% of the existing inventory, so EPA anticipates that at
least that much inventory could be available for critical uses during
2013.
EPA is also seeking comment on using the above approach but
allocating 0% from existing stocks for 2013 in light of the withdrawal
of iodomethane from the market. In March 2012, Arysta LifeScience, the
manufacturer of iodomethane, suspended the sale of iodomethane across
the United States. This alternative was registered for use in 48 states
on strawberries, tomatoes, peppers, ornamentals, turf, orchard replant,
forest nursery seedlings, and strawberry nurseries. Many users had been
transitioning to this alternative since 2008, when the product was
federally registered.
EPA believes that the unanticipated loss of this alternative could
have increased demand for methyl bromide in 2012 from critical users.
In comments to EPA's 2010 CUE Rule, Arysta provided data that 97,341 kg
of iodomethane was used in 2008 and 177,991 kg was used in 2009. They
calculated this to be equivalent to approximately 5,000 and 10,000
acres respectively. They also anticipated sales of 250,000 kg in 2010,
which would be equivalent to 650 MT of methyl bromide on 13,500 acres.
In 2012, critical users may seek additional methyl bromide from
pre-phaseout inventory than in previous years. The 2012 critical uses
include all of the registered uses of iodomethane except for turf.
Growers in Florida and the Southeastern United States were using
iodomethane on tomatoes, peppers, strawberries, and ornamentals. While
many of these sectors could use alternatives other than iodomethane,
such as the UGA 3-way, the unexpected loss of iodomethane could lead to
growers using inventory methyl bromide for this season. The historical
trend described below, in which no more than 70% of the CSAs allocated
in one year had ever been expended, may not hold true for 2012.
However, under the framework, the use of inventory for critical uses
cannot exceed the total CSA allocation of 263 MT in 2012.
EPA also does not believe that the withdrawal of iodomethane will
increase demand for pre-phaseout inventory from non-critical uses in
2012. Under the reregistration decision for methyl bromide, seven non-
critical uses remain on the pre-plant methyl bromide labels. These non-
critical uses can continue to use methyl bromide but are restricted to
pre-phaseout inventory. The uses are caneberries, fresh market tomatoes
grown in California, fresh market peppers grown in California, Vidalia
onions grown in Georgia, ginger grown in Hawaii, soils on golf courses
and athletic/recreational fields for resurfacing/replanting of turf,
and tobacco seedling trays. See 76 FR 7200 (February 9, 2011).
Collectively they are referred to as ``Group II uses.'' Of the Group II
uses, iodomethane was only registered for use on fresh market tomatoes
grown in California, fresh market peppers grown in California, and
turf. Iodomethane was not used in California and EPA suspects it was
not widely used on turf since that sector did not submit an application
for a critical use exemption for 2015. EPA is seeking comment and
additional data on whether the loss of iodomethane will limit the
availability of inventory in 2013.
EPA understands that changes in the status of methyl bromide
alternatives can occur, and that these changes may expand or contract
the list of existing options. We also understand that the sudden change
in the availability of iodomethane has created near-term difficulties
for growers in transition. As noted above, EPA has taken this change in
circumstance into account in proposing to allocate the full amount of
CUE authorized by the Parties in 2013. EPA is also requesting comment
on a range of potential amounts for the CSA allocation, recognizing
that past CUE rules may have overestimated the amount of stocks that
are available to critical users. Finally, EPA requests comment on and
relevant data to support consideration of other potential mechanisms
within the Clean Air Act or other statutory authorities that the EPA
could use to respond to unforeseen or emergency situations.
Therefore, under this proposed approach, the agency is proposing to
allocate 5% of existing inventory, or 62,444 kg of critical stock
allowances for 2013. EPA solicits comment on whether 5% is the
appropriate amount, or whether a higher or lower figure would be
appropriate. EPA specifically seeks comment on allocating 0 kg from
stocks under this approach. In considering the possibility of an
allocation for CSAs set at 0 kg, EPA is particularly interested in
comments from critical stock allowance holders who would be barred
under the existing framework from selling inventory to critical users
in 2013. EPA is interested in learning whether an allocation at or
close to 0 kg would prevent the drawdown of stocks or prevent the
fulfillment of contracts or commitments to sell pre-phaseout inventory
in 2013. EPA is interested in learning whether critical users who in
the past have accessed allocations of CSAs would still be able to
access methyl bromide, either through the conversion of CUAs to CSAs,
or from other sources. Finally, EPA is interested in comment on the
restriction in the framework rule that limits the sale of inventory to
critical uses through the CSA allocation, see 40 CFR 82.4(p), whether
that restriction should be lifted, and to what extent reporting and
recordkeeping requirements should be adjusted were the restriction
lifted.
Option 2: Framework Approach
EPA also solicits comment on whether it should retain for 2013 its
recent approach to calculating ``available stocks'' using the formula
ASCP = ESPP - DPP - SCFCP.
EPA calculates through this formula that there will be 221,495 kg of
``available stocks'' on January 1, 2013. Under this approach, EPA would
allocate 221,495 kg of CSAs for 2013.
The first step in the formula is to estimate the drawdown of stocks
during 2012. To do so, EPA adds the estimated amount of CSAs that will
be expended in 2012 plus the estimated amount of methyl bromide that
will be used in 2012 for non-critical uses. EPA believes that this is a
better practice than using a simple linear fit estimation, which
[[Page 74443]]
was the approach EPA used in the first few years it conducted this
analysis. A linear estimate would have projected that no methyl bromide
would remain in inventory at the beginning of 2013. Furthermore, this
estimate does not consider that the use of inventory on critical uses
is limited by the allocation of CSAs.
The first element of the drawdown estimate is the amount of
inventory used in 2012 on critical uses. This can be no more than the
number of CSAs EPA allocated in the 2012 CUE Rule, which is 263,082 kg.
As discussed in the Technical Support Document, on average only 59% of
the CSAs allocated for a control period are reported as sold in that
control period. To estimate the number of expended CSAs in 2012, EPA
conservatively assumes that 70% of the CSAs allocated for 2012 will be
sold. This amount is greater than any year's use of CSA allocations,
however EPA notes below that the loss of iodomethane may result in
greater demand for inventory in 2012 than past years. Thus, EPA
estimates that 184,157 kg of inventory will be sold for critical uses
in 2012.
The second element of the drawdown estimate is the amount of
inventory used in 2012 on Group II and non-critical uses. Group II uses
are seven non-critical uses that remain on the pre-plant methyl bromide
labels. Post-harvest labels have not been revised yet to implement the
terms of the reregistration decision concerning use of methyl bromide
for commodity fumigation and thus the universe of labeled post-harvest
uses remains broader.
There is no clear trend in the pattern of usage for non-critical
uses. EPA therefore is estimating the amount of sales for non-critical
uses in 2012 by analyzing the percent of the total inventory used each
year for this purpose. For example, in 2010, 36% of the total start of
year inventory was sold for non-critical uses. On a weight basis, this
was equal to 647 MT. In 2006, much more inventory (on a weight basis)
was sold for non-critical uses, 1,249 MT, but this comprised only 16%
of the total start of year inventory that year. EPA does not believe
that an average of the amounts sold (on a weight basis) in 2006-2011
for all non-critical uses is accurate because the inventory has
declined. For example, the 1,249 MT of inventory was sold in 2006 for
non-critical uses is unlikely to provide an accurate description of the
drawdown in 2012, even when averaged with other years' data, because
there was only 1,249 MT of inventory at the beginning of 2012. EPA
therefore is analyzing the drawdown on a proportional basis rather than
a strictly weight basis. While the average proportion is 17%, EPA is
conservatively using the highest proportion. Therefore, EPA estimates
that 36% of the total start of year inventory would be used for non-
critical uses in 2012. Thus, EPA estimates that 449,595 kg of inventory
will be sold for Group II uses in 2012. EPA believes that this estimate
is conservative because the analysis encompasses years where the use of
inventory included all non-critical uses, and was not restricted to
Group II uses. These data are contained in EPA's annual Accounting
Frameworks submitted to UNEP and summarized in the technical support
document in the docket.
In summary, EPA estimates the drawdown of inventory in 2012 as the
sum of (1) the use of CSAs in 2012 and (2) the estimate for non-
critical uses in 2012. Using this method, EPA conservatively projects
that the pre-phaseout methyl bromide inventory will be drawn down by
633,759 kg (184,157 + 449,595) during 2012. This would result in a pre-
phaseout inventory declining from 1,248,876 kg on January 1, 2012, to
615,124 kg on January 1, 2013. EPA welcomes comment on this proposed
method of calculating inventory drawdown. If EPA utilizes this approach
in the final rule and receives actual end-of-year reported data on
inventory levels before this rule is finalized, EPA may substitute that
data for this estimate.
The next element in the calculation of available stocks is the
supply chain factor (SCF). The SCF represents EPA's technical estimate
of the amount of pre-phaseout inventory that would be adequate to meet
a need for critical use methyl bromide after an unforeseen domestic
production failure. As described in the 2008 CUE Rule, and the
Technical Support Document contained in the docket to this rule, EPA
estimates that it would take 15 weeks for significant imports of methyl
bromide to reach the U.S in the event of a major supply disruption.
Consistent with the regulatory framework used in previous CUE
allocation rules, the SCF for 2013 conservatively reflects the effect
of a supply disruption occurring in the peak period of critical use
methyl bromide production, which is the first quarter of the year.
While this 15-week disruption is based on shipping capacity and does
not change year to year, other inputs to EPA's analysis do change each
year including the total U.S. and global authorizations for methyl
bromide and the average seasonal production of critical use methyl
bromide in the United States. Using updated numbers, EPA estimates that
critical use production in the first 15 weeks of each year (the peak
supply period) currently accounts for approximately 70% of annual
critical use methyl bromide demand. EPA, therefore, estimates that the
peak 15-week shortfall in 2013 could be 394 MT.
As EPA stated in previous CUE Rules, the SCF is not a ``reserve''
of methyl bromide but is merely an analytical tool used to provide
greater transparency regarding how the Agency determines CSA amounts.
Further general discussion of the SCF is in the final 2008 CUE rule (72
FR 74118, December 28, 2007) and further detail about the analysis used
to derive the value for the 2013 supply chain factor is provided in the
Technical Support Document available on the public docket for this
rulemaking.
Using the formula AS2013 = ES2012-
D2012-SCF2013, EPA estimates under the framework
approach that there will be 221,495 kg of pre-phaseout stocks of methyl
bromide ``available'' to be allocated in 2013. (221,495 = 1,248,876 -
633,759 - 393,628). EPA welcomes comment on this approach to
determining the level of available stocks and the critical stock
allowance allocation for 2013.
In summary, EPA is proposing for 2013 a new approach for allocating
amounts authorized for critical uses between CSAs and CUAs, by
allocating CSAs as a percentage of the existing inventory. In
particular, EPA is proposing to allocate CSAs in an amount equal to 5%
of the 2012 reported inventory, or 62,444 kg. EPA seeks comment on a
range of values for the allocation of CSAs, given the loss of
iodomethane. EPA particularly solicits comment on allocating 0 kg of
CSAs. EPA is also seeking comment on using the existing framework to
calculate the amount of ``available stocks'' in 2013. EPA estimates the
CSA allocation would be 221,495 kg under this approach.
As in past years, EPA would allocate CSAs based on each company's
proportionate share of the aggregate inventory. In 2006, the United
States District Court for the District of Columbia upheld EPA's
treatment of company-specific methyl bromide inventory information as
confidential. NRDC v. Leavitt, 2006 WL 667327 (D.D.C. March 14, 2006).
Therefore, the documentation regarding company-specific allocation of
CSAs is in the confidential portion of the rulemaking docket and the
individual CSA allocations are not listed in the table in 40 CFR
82.8(c)(2). EPA will inform listed companies of their CSA
[[Page 74444]]
allocations in a letter following publication of the final rule.
2. Approach for Determining New Production and Import Allowances
For 2013, EPA is proposing to generally apply the existing
framework established in the Framework Rule. Under this approach, the
amount of new production would equal the total amount authorized by the
Parties to the Montreal Protocol in Decision XXIII/4, minus the CSA
amount detailed above, minus any reductions for carryover and the
uptake of alternatives. As explained above, EPA has considered a number
of factors in determining the total allocation, including the loss of
the alternative iodomethane, and is not proposing to reduce the total
allocation below the amount approved in Decision XXIII/4. Applying this
established approach, EPA is proposing to exempt limited amounts of new
production and import of methyl bromide for critical uses in 2013 such
that the total authorization equals 562,326 kg. Because EPA is taking
comment on a range of values for the critical stock allocation, there
would be a corresponding range of values for the new production/import
amount from to 340,831 kg to 562,326 kg. EPA is proposing an approach
that would result in an allocation of 499,882 kg. EPA is taking comment
on this approach.
Carryover Material The Parties in paragraph 6 of Decision XXIII/4
``urge parties operating under critical-use exemptions to put in place
effective systems to discourage the accumulation of methyl bromide
produced under the exemption.'' As discussed in the Framework Rule, EPA
regulations prohibit methyl bromide produced or imported after January
1, 2005, under the critical use exemption being added to the existing
pre-2005 inventory. Quantities of methyl bromide produced, imported,
exported, or sold to end-users under the critical use exemption in a
control period must be reported to EPA the following year. EPA uses
these reports to calculate the amount of methyl bromide produced or
imported under the critical use exemption, but not exported or sold to
end-users in that year. EPA deducts an amount equivalent to this
``carryover'' from the total level of allowable new production and
import in the year following the year of the data report. Carryover
material (which is produced using critical use allowances) is not
included in EPA's definition of existing inventory (which applies to
pre-2005 material) because this would lead to a double-counting of
carryover amounts, and a double reduction of critical use allowances
(CUAs).
All critical use methyl bromide that companies reported to be
produced or imported in 2011 was sold to end users. The information
reported to EPA is that 1,499 MT of critical use methyl bromide was
produced or imported in 2011. Slightly more than the amount produced or
imported was actually sold to end-users. This additional amount was
from distributors selling material that was carried over from the prior
control period. Using the existing framework, EPA is proposing to apply
the carryover deduction of 0 kg to the new production amount. EPA's
calculation of the amount of carryover at the end of 2011 is consistent
with the method used in previous CUE rules, and with the method agreed
to by the Parties in Decision XVI/6 for calculating column L of the
U.S. Accounting Framework. Past U.S. Accounting Frameworks, including
the one for 2011, are available in the public docket for this
rulemaking.
Uptake of Alternatives Under the existing framework, EPA considers
data on the availability of alternatives that it receives following
submission of each nomination to UNEP. In previous rules EPA has
reduced the total CUE amount when a new alternative has been
registered. Because EPA determines the CSA allocation separately, any
reduction in the total amount has been reflected in a corresponding
reduction in the allocation for new production/import. However, where
an alternative is withdrawn, EPA cannot propose to increase the total
CUE amount above the amount authorized by the Parties.
A development since the USG submitted the 2013 CUN is that Dimethyl
Disulfide (DMDS) has been registered in additional states. In July
2010, EPA registered DMDS to control nematodes, weeds, and pathogens in
tomatoes, peppers, eggplants, curcurbits, strawberries, ornamentals and
forest nursery seedlings, and onions. The CUN considered only a limited
uptake in 2013. At that time only a few states had registered DMDS and
it was not registered in either California or Florida. Twenty-four
states have now registered DMDS, including Georgia and Florida.
EPA is proposing not to make a reduction to the new production/
import allocation based on these additional state registrations. As
discussed above, over 90% of the amount authorized is for critical uses
in California, which has not yet registered DMDS. EPA anticipates that
the uptake of DMDS in the Southeast will therefore not significantly
affect total demand for critical use methyl bromide.
EPA is not proposing to make any other modifications for
alternatives. Transition rates for other alternatives have already been
applied for authorized 2013 critical use amounts through the nomination
and authorization process. EPA will consider new data received during
the comment period and continues to gather information about methyl
bromide alternatives through the CUE application process, and by other
means. EPA also continues to support research and adoption of methyl
bromide alternatives, and to request information about the economic and
technical feasibility of all existing and potential alternatives.
Allocation Amounts EPA is proposing to allocate 2013 critical use
allowances for new production or import of methyl bromide equivalent to
499,882 kg. Because EPA is proposing a range of approaches for the
critical stock allocation, EPA is taking comment on the corresponding
range of values for the new production/import amount from to 340,831 kg
to 562,326 kg.
EPA is proposing to allocate allowances to the four companies that
hold baseline allowances. The proposed allocation, as in previous
years, is in proportion to those baseline amounts, as shown in the
proposed changes to the table in 40 CFR 82.8(c)(1). Paragraph 3 of
Decision XXIII/4 states ``that parties shall endeavor to license,
permit, authorize or allocate quantities of methyl bromide for critical
uses as listed in table A of the annex to the present decision.'' This
is similar to language in prior Decisions authorizing critical uses.
These Decisions call on Parties to endeavor to allocate critical use
methyl bromide on a sector basis. The Framework Rule proposed several
options for allocating critical use allowances, including a sector-by-
sector approach. The agency evaluated various options based on their
economic, environmental, and practical effects. After receiving
comments, EPA determined that a lump-sum, or universal, allocation,
modified to include distinct caps for pre-plant and post-harvest uses,
was the most efficient and least burdensome approach that would achieve
the desired environmental results, and that a sector-by-sector approach
would pose significant administrative and practical difficulties. For
the reasons discussed in the preamble to the 2009 CUE rule (74 FR
19894), the agency believes that under the approach adopted in the
Framework Rule, the actual critical use
[[Page 74445]]
will closely follow the sector breakout listed in the Parties'
decisions.
F. The Criteria in Decisions IX/6 and Ex. I/4
Paragraphs 1 and 4 of Decision XXIII/4 request Parties to ensure
that the conditions or criteria listed in Decisions Ex. I/4 and IX/6,
paragraph 1, are applied to exempted critical uses for the 2013 control
period. A discussion of the agency's application of the criteria in
paragraph 1 of Decision IX/6 appears in sections V.A., V.D., and V.E.
of this preamble. In section V.D. the agency solicits comments on the
technical and economic basis for determining that the uses listed in
this proposed rule meet the criteria of the critical use exemption. The
CUNs detail how each proposed critical use meets the criteria listed in
paragraph 1 of Decision IX/6, apart from the criterion located at
(b)(ii), as well as the criteria in paragraphs 5 and 6 of Decision Ex.
I/4.
The criterion in Decision IX/6(1)(b)(ii), which refers to the use
of available stocks of methyl bromide, is addressed in section V.E. of
this preamble. The agency has previously provided its interpretation of
the criterion in Decision IX/6(1)(a)(i) regarding the presence of
significant market disruption in the absence of an exemption, and EPA
refers readers to the 2006 CUE final rule (71 FR 5989, February 6,
2006) as well as to the memo on the docket ``Development of 2003
Nomination for a Critical Use Exemption for Methyl Bromide for the
United States of America'' for further elaboration.
The remaining considerations, including the lack of available
technically and economically feasible alternatives under the
circumstance of the nomination; efforts to minimize use and emissions
of methyl bromide where technically and economically feasible; the
development of research and transition plans; and the requests in
Decision Ex. I/4(5) and (6) that Parties consider and implement MBTOC
recommendations, where feasible, on reductions in the critical use of
methyl bromide and include information on the methodology they use to
determine economic feasibility, are addressed in the nomination
documents.
Some of these criteria are evaluated in other documents as well.
For example, the United States has further considered matters regarding
the adoption of alternatives and research into methyl bromide
alternatives, criterion (1)(b)(iii) in Decision IX/6, in the
development of the National Management Strategy submitted to the Ozone
Secretariat in December 2005, updated in October 2009, as well as in
ongoing consultations with industry. The National Management Strategy
addresses all of the aims specified in Decision Ex.I/4(3) to the extent
feasible and is available in the docket for this rulemaking.
There continues to be a need for methyl bromide in order to conduct
the research required by Decision IX/6. A common example is an outdoor
field experiment that requires methyl bromide as a standard control
treatment with which to compare the trial alternatives' results. As
discussed in the preamble to the 2010 CUE rule (75 FR 23179, May 3,
2010), research is a key element of the critical use process. Research
on the crops shown in the table in Appendix L to subpart A remains a
critical use of methyl bromide. While researchers may continue to use
newly produced material for field, post-harvest, and emission
minimization studies requiring the use of methyl bromide, EPA
encourages researchers to use pre-phaseout inventory purchased through
the expenditure of CSAs. EPA also encourages distributors to make
inventory available to researchers, to promote the continuing effort to
assist growers to transition critical use crops to alternatives.
G. Emissions Minimization
Previous decisions have stated that critical users shall employ
emission minimization techniques such as virtually impermeable films,
barrier film technologies, deep shank injection and/or other techniques
that promote environmental protection, whenever technically and
economically feasible. EPA developed a comprehensive strategy for risk
mitigation through the 2006 Reregistration Eligibility Decision (RED)
for methyl bromide, which is implemented through restrictions on how
methyl bromide products can be used. This approach requires that methyl
bromide labels include directions that treated sites be tarped except
for California orchard replant where EPA instead requires deep (18
inches or greater) shank applications. The RED also incorporated
incentives for applicators to use high-barrier tarps, such as virtually
impermeable film (VIF), by allowing smaller buffer zones around those
sites. In addition to minimizing emissions, use of high-barrier tarps
has the benefit of providing pest control at lower application rates.
The amount of methyl bromide nominated by the United States reflects
the lower application rates necessary when using high-barrier tarps,
where such tarps are allowed.
EPA will continue to work with the U.S. Department of Agriculture--
Agricultural Research Service (USDA-ARS) and the National Institute for
Food and Agriculture (USDA-NIFA) to promote emission reduction
techniques. The federal government has invested substantial resources
into best practices for methyl bromide use, including emission
reduction practices. The Cooperative Extension System, which receives
some support from USDA-NIFA provides locally appropriate and project
focused outreach education regarding methyl bromide transition best
practices. Additional information on USDA research on alternatives and
emissions reduction can be found at: https://www.ars.usda.gov/research/programs/programs.htm?NP_CODE=308 and https://www.csrees.usda.gov/fo/methylbromideicgp.cfm.
Users of methyl bromide should continue to make every effort to
minimize overall emissions of methyl bromide to the extent consistent
with State and local laws and regulations. EPA also encourages
researchers and users who are using such techniques to inform EPA of
their experiences and to provide such information with their critical
use applications.
VI. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review and Executive
Order 13563: Improving Regulation and Regulatory Review
Under Executive Order (EO) 12866 (58 FR 51735, October 4, 1993),
this proposal is a ``significant regulatory action.'' This action is
likely to result in a rule that may raise novel legal or policy issues.
Accordingly, EPA submitted this action to the Office of Management and
Budget (OMB) for review under Executive Orders 12866 and 13563 (76 FR
3821, January 21, 2011) and any changes made in response to interagency
recommendations have been documented in the docket for this action.
B. Paperwork Reduction Act
This action does not impose any new information collection burden.
The application, recordkeeping, and reporting requirements have already
been established under previous critical use exemption rulemakings and
this action does not propose to change any of those existing
requirements. The Office of Management and Budget (OMB) has previously
approved the information collection requirements contained in the
existing regulations at
[[Page 74446]]
40 CFR part 82 under the provisions of the Paperwork Reduction Act, 44
U.S.C. 3501 et seq. and has assigned OMB control number 2060-0482. The
OMB control numbers for EPA's regulations in 40 CFR are listed in 40
CFR part 9.
C. Regulatory Flexibility Act
The RFA generally requires an agency to prepare a regulatory
flexibility analysis of any rule subject to notice-and-comment
rulemaking requirements under the Administrative Procedure Act or any
other statute unless the agency certifies that the rule will not have a
significant economic impact on a substantial number of small entities.
Small entities include small businesses, small organizations, and small
governmental jurisdictions. For purposes of assessing the impacts of
this rule on small entities, small entity is defined as: (1) A small
business as defined by the Small Business Administration's regulations
at 13 CFR 121.201 (see Table below); (2) a small governmental
jurisdiction that is a government of a city, county, town, school
district or special district with a population of less than 50,000; and
(3) a small organization that is any not-for-profit enterprise which is
independently owned and operated and is not dominant in its field.
----------------------------------------------------------------------------------------------------------------
NAICS Small business size standard
Category NAICS code SIC code (in number of employees or
millions of dollars)
----------------------------------------------------------------------------------------------------------------
Agricultural production....... 1112--Vegetable and 0171--Berry Crops.... $0.75 million.
Melon farming.
1113--Fruit and Nut 0172--Grapes.........
Tree Farming.
1114--Greenhouse, 0173--Tree Nuts......
Nursery, and
Floriculture
Production.
0175--Deciduous Tree
Fruits (except apple
orchards and farms).
0179--Fruit and Tree
Nuts, NEC.
0181--Ornamental
Floriculture and
Nursery Products.
0831--Forest
Nurseries and
Gathering of Forest
Products.
Storage Uses.................. 115114--Postharvest ..................... $7 million.
Crop activities
(except Cotton
Ginning).
311211--Flour Milling 2041--Flour and Other 500 employees.
Grain Mill Products.
311212--Rice Milling. 2044--Rice Milling... 500 employees.
493110--General 4225--General $25.5 million.
Warehousing and Warehousing and
Storage. Storage.
493130--Farm Product 4221--Farm Product $25.5 million.
Warehousing and Warehousing and
Storage. Storage.
Distributors and Applicators.. 115112--Soil 0721--Crop Planting, $7 million.
Preparation, Cultivation, and
Planting and Protection.
Cultivating.
Producers and Importers....... 325320--Pesticide and 2879--Pesticides and 500 employees.
Other Agricultural Agricultural
Chemical Chemicals, NEC.
Manufacturing.
----------------------------------------------------------------------------------------------------------------
Agricultural producers of minor crops and entities that store
agricultural commodities are categories of affected entities that
contain small entities. This proposed rule would only affect entities
that applied to EPA for an exemption to the phaseout of methyl bromide.
In most cases, EPA received aggregated requests for exemptions from
industry consortia. On the exemption application, EPA asked consortia
to describe the number and size distribution of entities their
application covered. EPA estimated that 3,218 entities petitioned EPA
for an exemption for the 2005 control period. EPA revised this estimate
in 2011 down to 1,800 end users of critical use methyl bromide. EPA
believes that the number continues to decline as growers cease applying
for critical uses. Since many applicants did not provide information on
the distribution of sizes of entities covered in their applications,
EPA estimated that, based on the above definition, between one-fourth
and one-third of the entities may be small businesses. In addition,
other categories of affected entities do not contain small businesses
based on the above description.
After considering the economic impacts of this proposed rule on
small entities, I certify that this action will not have a significant
economic impact on a substantial number of small entities. In
determining whether a rule has a significant economic impact on a
substantial number of small entities, the impact of concern is any
significant adverse economic impact on small entities, since the
primary purpose of the regulatory flexibility analyses is to identify
and address regulatory alternatives ``which minimize any significant
economic impact of the proposed rule on small entities.'' (5 U.S.C.
603-604). Thus, an agency may certify that a rule will not have a
significant economic impact on a substantial number of small entities
if the rule relieves a regulatory burden, or otherwise has a positive
economic effect on all of the small entities subject to the rule. Since
this rule would allow the use of methyl bromide for approved critical
uses after the phaseout date of January 1, 2005, this action would
confer a benefit to users of methyl bromide. EPA estimates in the
Regulatory Impact Assessment found in the docket to this rule that the
reduced costs resulting from the de-regulatory creation of the
exemption are approximately $22 million to $31 million on an annual
basis (using a 3% or 7% discount rate respectively). We have therefore
concluded that this proposed rule would relieve regulatory burden for
all small entities.
D. Unfunded Mandates Reform Act
This action contains no Federal mandates under the provisions of
Title II of the Unfunded Mandates Reform Act of 1995 (UMRA), 2 U.S.C.
1531-1538 for State, local, or tribal governments or the private
sector. The action imposes no enforceable duty on any State, local or
tribal governments or the private sector. Instead, this action would
provide an exemption for the manufacture and use of a phased out
compound and would not impose any new requirements on any entities.
[[Page 74447]]
Therefore, this action is not subject to the requirements of sections
202 or 205 of the UMRA. This action is also not subject to the
requirements of section 203 of UMRA because it contains no regulatory
requirements that might significantly or uniquely affect small
governments.
E. Executive Order 13132: Federalism
This action does not have federalism implications. It will not have
substantial direct effects on the States, on the relationship between
the national government and the States, or on the distribution of power
and responsibilities among the various levels of government, as
specified in Executive Order 13132. This proposed rule is expected to
primarily affect producers, suppliers, importers, and exporters and
users of methyl bromide. Thus, Executive Order 13132 does not apply to
this proposed rule. In the spirit of Executive Order 13132, and
consistent with EPA policy to promote communications between EPA and
State and local governments, EPA specifically solicits comment on this
proposed action from State and local officials.
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). This rule does
not significantly or uniquely affect the communities of Indian tribal
governments nor does it impose any enforceable duties on communities of
Indian tribal governments. Thus, Executive Order 13175 does not apply
to this action. EPA specifically solicits additional comment on this
proposed action from tribal officials.
G. Executive Order No. 13045: Protection of Children From Environmental
Health and Safety Risks
EPA interprets EO 13045 (62 FR 19885, April 23, 1997) as applying
only to those regulatory actions that concern health or safety risks,
such that the analysis required under section 5-501 of the EO has the
potential to influence the regulation. This action is not subject to EO
13045 because it does not establish an environmental standard intended
to mitigate health or safety risks.
H. Executive Order 13211: Actions That Significantly Affect Energy
Supply, Distribution, or Use
This proposed rule is not a ``significant energy action'' as
defined in Executive Order 13211, ``Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use'' (66 FR 28355
(May 22, 2001)) because it is not likely to have a significant adverse
effect on the supply, distribution, or use of energy. This proposed
rule does not pertain to any segment of the energy production economy
nor does it regulate any manner of energy use. Therefore, we have
concluded that this proposed rule is not likely to have any adverse
energy effects.
I. National Technology Transfer and Advancement Act
Section 12(d) of the National Technology Transfer and Advancement
Act of 1995 (``NTTAA''), Public Law 104-113, 12(d) (15 U.S.C. 272 note)
directs EPA to use voluntary consensus standards in its regulatory
activities unless to do so would be inconsistent with applicable law or
otherwise impractical. Voluntary consensus standards are technical
standards (e.g., materials specifications, test methods, sampling
procedures, and business practices) that are developed or adopted by
voluntary consensus standards bodies. NTTAA directs EPA to provide
Congress, through OMB, explanations when the agency decides not to use
available and applicable voluntary consensus standards. This proposed
rulemaking does not involve technical standards. Therefore, EPA is not
considering the use of any voluntary consensus standards.
J. Executive Order 12898: Federal Actions To Address Environmental
Justice in Minority Populations and Low-Income Populations
Executive Order (EO) 12898 (59 FR 7629 (Feb. 16, 1994)) establishes
federal executive policy on environmental justice. Its main provision
directs federal agencies, to the greatest extent practicable and
permitted by law, to make environmental justice part of their mission
by identifying and addressing, as appropriate, disproportionately high
and adverse human health or environmental effects of their programs,
policies, and activities on minority populations and low-income
populations in the United States.
EPA has determined that this proposed rule will not have
disproportionately high and adverse human health or environmental
effects on minority or low-income populations, because it affects the
level of environmental protection equally for all affected populations
without having any disproportionately high and adverse human health or
environmental effects on any population, including any minority or low-
income population. Any ozone depletion that results from this proposed
rule will impact all affected populations equally because ozone
depletion is a global environmental problem with environmental and
human effects that are, in general, equally distributed across
geographical regions in the United States.
List of Subjects in 40 CFR Part 82
Environmental protection, Chemicals, Exports, Imports, Ozone
depletion.
Dated: December 7, 2012.
Lisa P. Jackson,
Administrator.
For the reasons stated in the preamble, 40 CFR Part 82 is proposed
to be amended as follows:
PART 82--PROTECTION OF STRATOSPHERIC OZONE
1. The authority citation for part 82 continues to read as follows:
Authority: 42 U.S.C. 7414, 7601, 7671-7671q.
2. Amend Sec. 82.8 by revising the table in paragraph (c)(1) and
by revising paragraph (c)(2).
Sec. 82.8 Grant of essential use allowances and critical use
allowances.
* * * * *
(c) * * *
(1) * * *
------------------------------------------------------------------------
2013 Critical use
2013 Critical use allowances for
Company allowances for post-harvest
pre-plant uses* uses*
(kilograms) (kilograms)
------------------------------------------------------------------------
Great Lakes Chemical Corp. A 287,633 16,145
Chemtura Company.................
Albemarle Corp.................... 118,281 6,639
ICL-IP America.................... 65,365 3,669
TriCal, Inc....................... 2,035 114
-------------------------------------
[[Page 74448]]
Total**....................... 473,315 26,567
------------------------------------------------------------------------
* For production or import of Class I, Group VI controlled substance
exclusively for the Pre-Plant or Post-Harvest uses specified in
appendix L to this subpart.
** Due to rounding, numbers do not add exactly.
(2) Allocated critical stock allowances granted for specified
control period. The following companies are allocated critical stock
allowances for 2013 on a pro-rata basis in relation to the inventory
held by each.
----------------------------------------------------------------------------------------------------------------
----------------------------------------------------------------------------------------------------------------
Company
----------------------------------------------------------------------------------------------------------------
Albemarle Degesch America, Inc. Prosource One
Bill Clark Pest Control, Inc. Helena Chemical Co. Trical Inc.
Burnside Services, Inc. ICL-IP America Trident Agricultural Products
Cardinal Professional Products Industrial Fumigant Company TriEst Ag Group, Inc.
Chemtura Corp. Pacific Ag Supplies Inc. Univar
Crop Production Services Pest Fog Sales Corp. Western Fumigation
----------------------------------------------------------------------------------------------------------------
TOTAL-62,444 kilograms
----------------------------------------------------------------------------------------------------------------
3. Appendix L to Subpart A is revised to read as follows:
Appendix L to Subpart A of Part 82--Approved Critical Uses and Limiting
Critical Conditions for Those Uses for the 2013 Control Period
--------------------------------------------------------------------------------------------------------------------------------------------------------
Column A Column B Column C
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Approved critical user and Limiting critical conditions that exist, or that the approved critical user
Approved critical uses location of use reasonably expects could rise without methyl bromide fumigation:
--------------------------------------------------------------------------------------------------------------------------------------------------------
PRE-PLANT USES
--------------------------------------------------------------------------------------------------------------------------------------------------------
Cucurbits........................... Georgia growers on fewer Moderate to severe yellow or purple nutsedge infestation.
than 10 acres. Moderate to severe soilborne disease infestation.
Moderate to severe root knot nematode infestation.
Eggplant............................ (a) Florida growers......... Moderate to severe yellow or purple nutsedge infestation.
Moderate to severe soilborne disease infestation.
Restrictions on alternatives due to karst topographical.
features and soils not supporting seepage irrigation.
(b) Georgia growers on fewer Moderate to severe yellow or purple nutsedge infestation.
than 10 acres. Moderate to severe nematode infestation.
Moderate to severe pythium collar, crown and root rot.
Moderate to severe southern blight infestation.
Restrictions on alternatives due to karst topographical features.
Nursery Stock (Fruit, Nut, Flower).. Members of the California Moderate to severe nematode infestation.
Association of Nursery and Medium to heavy clay soils.
Garden Centers representing Local township limits prohibiting 1,3-dichloropropene.
Deciduous Tree Fruit
Growers.
Orchard Replant..................... California stone fruit, Moderate to severe nematode infestation.
table and raisin grape, Moderate to severe soilborne disease infestation.
wine grape, walnut, and Replanted orchard soils to prevent orchard replant disease.
almond growers. Medium to heavy soils.
Local township limits prohibiting 1,3-dichloropropene.
Ornamentals......................... (a) California growers...... Moderate to severe soilborne disease infestation.
Moderate to severe nematode infestation.
Local township limits prohibiting 1,3-dichloropropene.
(b) Florida growers......... Moderate to severe weed infestation.
Moderate to severe soilborne disease infestation.
Moderate to severe nematode infestation.
Restrictions on alternatives due to karst topographical.
features and soils not supporting seepage irrigation.
Peppers............................. (a) Florida growers......... Moderate to severe yellow or purple nutsedge infestation.
Moderate to severe soilborne disease infestation.
Moderate to severe nematode infestation.
Restrictions on alternatives due to karst topographical.
features and soils not supporting seepage irrigation.
[[Page 74449]]
(b) Georgia growers on fewer Moderate to severe yellow or purple nutsedge infestation.
than 10 acres. Moderate to severe nematode infestation, or moderate to severe pythium root and
collar rots.
Moderate to severe southern blight infestation, crown or root rot.
Restrictions on alternatives due to karst topographical features.
Strawberry Fruit.................... California growers.......... Moderate to severe black root rot or crown rot.
Moderate to severe yellow or purple nutsedge infestation.
Moderate to severe nematode infestation.
Local township limits prohibiting 1,3-dichloropropene.
Time to transition to an alternative.
Strawberry Nurseries................ California growers.......... Moderate to severe soilborne disease infestation.
Moderate to severe yellow or purple nutsedge infestation.
Moderate to severe nematode infestation.
Tomatoes............................ (a) Florida growers......... Moderate to severe yellow or purple nutsedge infestation.
Moderate to severe soilborne disease infestation.
Moderate to severe nematode infestation.
Restrictions on alternatives due to karst topographical.
features and soils not supporting seepage irrigation.
(b) Georgia growers on fewer Moderate to severe yellow or purple nutsedge infestation.
than 10 acres. Moderate to severe soilborne disease infestation.
Moderate to severe nematode infestation.
Restrictions on alternatives due to karst topographical features.
--------------------------------------------------------------------------------------------------------------------------------------------------------
POST-HARVEST USES
--------------------------------------------------------------------------------------------------------------------------------------------------------
Food Processing..................... (a) Rice millers in the U.S. Moderate to severe beetle, weevil, or moth infestation.
who are members of the USA Presence of sensitive electronic equipment subject to corrosion.
Rice Millers Association. Time to transition to an alternative.
(b) Pet food manufacturing Moderate to severe beetle, moth, or cockroach infestation.
facilities in the U.S. who Presence of sensitive electronic equipment subject to corrosion.
are members of the Pet Food Time to transition to an alternative.
Institute.
(c) Members of the North Moderate to severe beetle infestation.
American Millers' Presence of sensitive electronic equipment subject to corrosion.
Association in the U.S.. Time to transition to an alternative.
Commodities......................... California entities storing Rapid fumigation required to meet a critical market window, such as during the
walnuts, dried plums, figs, holiday season.
raisins, and dates (in
Riverside county only) in
California.
Dry Cured Pork Products............. Members of the National Red legged ham beetle infestation.
Country Ham Association and Cheese/ham skipper infestation.
the Association of Meat Dermested beetle infestation.
Processors, Nahunta Pork Ham mite infestation.
Center (North Carolina),
and Gwaltney and Smithfield
Inc.
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[FR Doc. 2012-30225 Filed 12-13-12; 8:45 am]
BILLING CODE 6560-50-P