Exemption Under the Federal Insecticide, Fungicide, and Rodenticide Act for Certain Plant-Incorporated Protectants Derived From Plant Viral Coat Protein Gene(s) (PVCP-PIPs); Supplemental Proposal, 19590-19640 [E7-7297]
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Federal Register / Vol. 72, No. 74 / Wednesday, April 18, 2007 / Proposed Rules
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 174
[EPA–HQ–OPP–2006–0642; FRL–8100–7]
RIN 2070–AD49
Exemption Under the Federal
Insecticide, Fungicide, and
Rodenticide Act for Certain PlantIncorporated Protectants Derived From
Plant Viral Coat Protein Gene(s)
(PVCP-PIPs); Supplemental Proposal
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
hsrobinson on PROD1PC76 with PROPOSALS2
AGENCY:
SUMMARY: EPA is proposing to exempt
from Federal Insecticide, Fungicide, and
Rodenticide Act (FIFRA) requirements
plant-incorporated protectants derived
from plant viral coat protein genes
(PVCP-PIPs) when the PVCP-PIP meets
specified criteria. EPA is proposing this
exemption because the Agency believes
that the PVCP-PIPs covered by this
exemption would be of a character
which is unnecessary to be subject to
FIFRA in order to carry out the purposes
of the Act.
DATES: Comments must be received on
or before July 17, 2007.
ADDRESSES: Submit your comments,
identified by docket identification (ID)
number EPA–HQ–OPP–2006–0642, by
one of the following methods:
• Federal eRulemaking Portal: https://
www.regulations.gov/. Follow the online instructions for submitting
comments.
• Mail: Office of Pesticide Programs
(OPP) Regulatory Public Docket (7502P),
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001.
• Delivery: OPP Regulatory Public
Docket (7502P), Environmental
Protection Agency, Rm. S-4400, One
Potomac Yard (South Building), 2777 S.
Crystal Drive, Arlington, VA. Deliveries
are only accepted during the Docket’s
normal hours of operation (8:30 a.m. to
4 p.m., Monday through Friday,
excluding legal holidays). Special
arrangements should be made for
deliveries of boxed information. The
Docket telephone number is (703) 305–
5805.
Instructions: Direct your comments to
docket ID number EPA–HQ–OPP–2006–
0642. EPA’s policy is that all comments
received will be included in the docket
without change and may be made
available on-line at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
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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 regulations.gov or email. The Federal regulations.gov
website 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
e-mail comment directly to EPA without
going through regulations.gov, your email address will be automatically
captured and included as part of the
comment that is placed in the 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.
Docket: All documents in the docket
are listed in the docket 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,
is not placed on the Internet and will be
publicly available only in hard copy
form. Publicly available docket
materials are available either in the
electronic docket at https://
www.regulations.gov, or, if only
available in hard copy, at the OPP
Regulatory Public Docket in Rm. S-4400,
One Potomac Yard (South Building),
2777 S. Crystal Drive, Arlington, VA.
The hours of operation of this Docket
Facility are from 8:30 a.m. to 4 p.m.,
Monday through Friday, excluding legal
holidays. The Docket telephone number
is (703) 305–5805.
FOR FURTHER INFORMATION CONTACT:
Melissa Kramer, Hazard Assessment
Coordination and Policy Division
(7202M), Office of Science Coordination
and Policy, 1200 Pennsylvania Ave.
NW, Washington, DC 20460–0001;
telephone number: (202) 564–8497; fax
number: (202) 564–8502; e-mail address:
kramer.melissa@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does This Notice Apply to Me?
You may be potentially affected by
this action if you are a person or
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company involved with agricultural
biotechnology that may develop and
market plant-incorporated protectants.
Potentially affected entities may
include, but are not limited to:
• Pesticide and Other Agricultural
Chemical Manufacturing (NAICS code
32532), e.g., establishments primarily
engaged in the formulation and
preparation of agricultural and
household pest control chemicals;
• Crop Production (NAICS code 111),
e.g., establishments primarily engaged
in growing crops, plants, vines, or trees
and their seeds;
• Colleges, Universities, and
Professional Schools (NAICS code
611310), e.g., establishments of higher
learning which are engaged in
development and marketing of virusresistant plants;
• Research and Development in the
Physical, Engineering, and Life Sciences
(NAICS code 54171), e.g., establishment
primarily engaged in conducting
research in the physical, engineering, or
life sciences, such as agriculture and
biotechnology.
This listing is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
affected by this action. Other types of
entities not listed in this unit could also
be affected. The North American
Industrial Classification System
(NAICS) codes have been provided to
assist you and others in determining
whether this action might apply to
certain entities. To determine whether
you or your business may be affected by
this action, you should carefully
examine the applicability provisions in
40 CFR part 174. If you have any
questions regarding the applicability of
this action to a particular entity, consult
the person listed under FOR FURTHER
INFORMATION CONTACT.
B. What Should I Consider as I Prepare
My Comments for EPA?
1. Docket. EPA has established a
docket for this action under docket
identification (ID) number EPA–HQ–
OPP–2006–0642. Publicly available
docket materials are available either in
the electronic docket at https://
www.regulations.gov, or, if only
available in hard copy, at the Office of
Pesticide Programs (OPP) Regulatory
Public Docket in Rm. S-4400, One
Potomac Yard (South Building), 2777 S.
Crystal Drive Arlington, VA. The hours
of operation of this Docket Facility are
from 8:30 a.m. to 4 p.m., Monday
through Friday, excluding legal
holidays. The Docket telephone number
is (703) 305–5805.
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2. Tips for preparing your comments.
When submitting comments, remember
to:
i. Identify the document by docket ID
number and other identifying
information (subject heading, Federal
Register date, and page number).
ii. 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.
iii. Explain why you agree or disagree;
suggest alternatives and substitute
language for your requested changes.
iv. Describe any assumptions and
provide any technical information and/
or data that you used.
v. If you estimate potential costs or
burdens, explain how you arrived at
your estimate in sufficient detail to
allow for it to be reproduced.
vi. Provide specific examples to
illustrate your concerns and suggest
alternatives.
vii. Explain your views as clearly as
possible, avoiding the use of profanity
or personal threats.
viii. Make sure to submit your
comments by the comment period
deadline identified.
II. Background
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A. What Action is the Agency
Proposing?
EPA is proposing an exemption from
FIFRA for certain plant virus coat
protein plant-incorporated protectants
or ‘‘PVCP-PIPs.’’ EPA is proposing to
define a PVCP-PIP as ‘‘a plantincorporated protectant derived from
one or more genes that encode a coat
protein of a virus that naturally infects
plants. This includes plant-incorporated
protectants derived from one or more
plant viral coat protein genes that
produce only RNA and no virus-related
protein.’’ PVCP-PIPs introduced into
plants with the intention of preventing
or mitigating viral disease meet the
FIFRA section 2(u) definition of
‘‘pesticide’’ because they are introduced
into plants with the intention of
‘‘preventing, destroying, repelling, or
mitigating any pest...’’ (7 U.S.C. 136(u))
and plant viruses meet the FIFRA
section 2 definition of ‘‘pest’’ (7 U.S.C.
136(t)). EPA is proposing this exemption
because the Agency believes that the
PVCP-PIPs covered by this exemption
would be of a character which is
unnecessary to be subject to FIFRA in
order to carry out the purposes of the
Act.
A PIP can be exempt from the
requirements of FIFRA, other than the
adverse effects reporting requirements
of 40 CFR 174.71, if it meets all three
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of the requirements listed in 40 CFR
174.21. Section 174.21(a) requires that
the PIP meet the criteria listed in at least
one of the sections in §§ 174.25 through
174.50. Section 174.21(b) requires that
when the PIP is intended to be
produced and used in a crop used as
food, the residues of the PIP are either
exempted from the requirement of a
tolerance under FFDCA or no tolerance
would otherwise be required for the PIP.
Section 174.21(c) requires that an
exempt PIP must contain only those
inert ingredient(s) included on the list
codified at §§ 174.485 through 174.490.
(Reference to §§ 174.485 through
174.490 in § 174.21(c) is proposed to be
changed to refer to §§ 174.485 through
174.486 in today’s Proposed Rule.) See
Unit II.F. for further discussion of these
§ 174.21 criteria.
The rule proposed in today’s Federal
Register would establish 40 CFR 174.27,
which would contain three criteria that,
when met, would allow PVCP-PIPs to
meet the general requirement for
exemption for all PIPs listed at 40 CFR
174.21(a). Today’s Federal Register also
proposes to add several substances
known to be used as inert ingredients in
PIPs to 40 CFR part 174 subpart X,
thereby potentially expanding the
PVCP-PIPs that could meet the
conditions of § 174.21(c). A companion
document published elsewhere in
today’s Federal Register also proposes a
tolerance exemption for certain PVCPPIP residues, thereby potentially
expanding the PVCP-PIPs that could
meet the conditions of § 174.21(b).
The three criteria that EPA is
proposing to insert at 40 CFR 174.27 are
intended to address three issues that
may be associated with a PVCP-PIP.
These issues are:
• The potential for increased
weediness or invasiveness of the crop
plant containing the PVCP-PIP or any
wild or weedy relatives that could
acquire the PVCP-PIP through gene flow
thereby causing negative effects on
either the agro-ecosystem or natural
environments. This issue is addressed
in proposed § 174.27(a).
• The potential that viruses with
novel properties could develop through
novel viral interactions. This issue is
addressed in proposed § 174.27(b).
• The potential for human or
nontarget organism exposure to proteins
that have not previously existed in
nature and thus should be examined to
determine whether they have
potentially toxic or allergenic
properties. This issue is addressed in
proposed § 174.27(c).
In order to satisfy 40 CFR 174.21(a),
a PVCP-PIP would have to satisfy
proposed § 174.27(a), (b), and (c). The
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requirements at § 174.27(d) would also
have to be met to qualify for exemption.
Proposed § 174.27(a), (b), and (c) each
can be met in one of two ways: a
product developer may self-determine
that paragraph (1) of the criterion
applies (i.e., § 174.27(a)(1), (b)(1), or
(c)(1)) or the Agency may determine that
paragraph (2) of the criterion applies
(i.e., § 174.27(a)(2), (b)(2), or (c)(2),
respectively). Paragraph (1) of each
proposed criterion (i.e., § 174.27(a)(1),
(b)(1), and (c)(1)) describes an objective,
well-defined characteristic. Therefore,
the developer may determine whether
the PVCP-PIP meets the requirement.
Paragraph (2) of each proposed criterion
(i.e., § 174.27(a)(2), (b)(2), and (c)(2)) is
conditioned on an Agency
determination because it may involve
analysis of several types of information.
Each criterion may be satisfied either by
self determination under paragraph (1)
or Agency determination under
paragraph (2) irrespective of how the
other two criteria are satisfied; there is
no requirement that all three criteria
must be satisfied under either paragraph
(1) or paragraph (2) in order to qualify
for the exemption.
B. What is the Agency’s Authority for
Taking this Action?
This rule is promulgated under the
authority of FIFRA sections 3(a), 25(a),
and 25(b) (7 U.S.C. 136a(a), 136w(a),
and 136w(b)).
FIFRA section 3(a) states that, except
as provided by the Act, no person may
distribute or sell in the United States
any pesticide that is not registered
under the Act (7 U.S.C. 136(a)). FIFRA
section 2(u) defines ‘‘pesticide’’ as: ‘‘(1)
any substance or mixture of substances
intended for preventing, destroying,
repelling, or mitigating any pest, (2) any
substance or mixture of substances
intended for use as a plant regulator,
defoliant, or desiccant, and (3) any
nitrogen stabilizer...’’ (7 U.S.C. 136(u)).
Under FIFRA section 2(t), the term
‘‘pest’’ includes ‘‘(1) any insect, rodent,
nematode, fungus, weed, or (2) any
other form of terrestrial or aquatic plant
or animal life or virus, bacteria, or other
microorganism... which the
Administrator declares to be a pest...’’
subject to certain exceptions (7 U.S.C.
136(t)).
Before EPA may register a pesticide
under FIFRA, the applicant must show
that the pesticide ‘‘when used in
accordance with widespread and
commonly recognized practice... will
not generally cause unreasonable
adversese effects on the environment’’
(7 U.S.C. 136a(c)(5)(D)). The term
‘‘environment’’ includes ‘‘water, air,
land, and all plants and man and other
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animals living therein, and the
interrelationships which exist among
these’’ (7 U.S.C. 136(j)). FIFRA section
2(bb) defines the term ‘‘unreasonable
adverse effects on the environment’’ to
mean: ‘‘(1) any unreasonable risk to man
or the environment, taking into account
the economic, social, and environmental
costs and benefits of the use of any
pesticide, or (2) a human dietary risk
from residues that result from a use of
a pesticide in or on any food
inconsistent with the standard under
section 408 of the Federal Food, Drug,
and Cosmetic Act’’ (7 U.S.C. 136(bb)).
Although FIFRA requires the
registration of most pesticides, it also
authorizes the regulation of unregistered
pesticides. FIFRA section 3(a) provides
that, to the extent necessary to prevent
unreasonable adverse effects on the
environment, the Administrator may
limit the distribution, sale, or use of any
pesticide that is not registered under
section 3 of FIFRA, subject to an
experimental use permit under section 5
of FIFRA, or subject to an emergency
exemption under section 18 of FIFRA.
Pesticides that are ‘‘not registered’’
include pesticides that are exempt from
FIFRA requirements under section
25(b).
An unregistered pesticide may be
distributed or sold if it is exempted by
regulation under FIFRA section 25(b).
Under FIFRA section 25(b)(2), the
Agency can exempt pesticides from
some or all of the requirements of
FIFRA when the Agency determines
that the pesticide is ‘‘of a character
which is unnecessary to be subject to
[FIFRA] in order to carry out the
purposes of this Act’’ (7 U.S.C.
136w(b)(2)). EPA interprets section
25(b)(2) to authorize the Agency to
exempt a pesticide or category of
pesticides that EPA determines (1) poses
a low probability of risk to the
environment and (2) is not likely to
cause unreasonable adverse effects to
the environment even in the absence of
regulatory oversight under FIFRA. This
standard differs from the standard for
registration which considers only
whether the pesticide ‘‘when used in
accordance with widespread and
commonly recognized practice... will
not generally cause unreasonable
adverse effects on the environment’’ (7
U.S.C. 136a(c)(5)(D)).
In evaluating the first condition that
must be met for the Agency to exempt
a pesticide, i.e., whether use of the
pesticide poses a low probability of risk
to the environment, EPA considers the
extent of the potential risks caused by
use of the pesticide to the environment,
including humans and other animals,
plants, water, air and land. Potential
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risks to humans include dietary risks as
well as non-dietary risks such as those
resulting from occupational or
residential exposure to the pesticide.
EPA uses the FFDCA section 408
standard in evaluating dietary risks as
discussed in Unit II.C. of this preamble.
EPA will not exempt pesticides unless
they pose a low probability of risk to the
environment.
In evaluating the second condition
that must be met for the Agency to
exempt a pesticide, i.e., whether the use
of the pesticide is unlikely to cause
unreasonable adverse effects on the
environment even in the absence of
regulatory oversight under FIFRA, EPA
balances all the potential risks to human
health, including dietary risks (see Unit
II.C. of this preamble for discussion of
the FFDCA standard), and risks to the
remainder of the environment from use
of the pesticide against the potential
benefits associated with its use. In
balancing risks and benefits, EPA
considers the economic, social, and
environmental costs and benefits of the
use of the pesticide. If the pesticide
poses a low probability of risk to the
environment and is not likely to cause
unreasonable adverse effects to the
environment even in the absence of
regulatory oversight under FIFRA, EPA
may exempt the pesticide from
regulation under FIFRA.
C. What is the Relationship of FIFRA
Exemptions to the FFDCA Section 408
Standard?
Under FFDCA section 408(a), a
pesticide chemical residue in or on a
food (hereafter simply ‘‘in food’’) is not
considered safe unless EPA has issued
a tolerance for the residue and the
residue is within the established
tolerance limit or EPA has issued an
exemption from the requirement of a
tolerance for the residue (21 U.S.C.
346a(a)(1)). FFDCA section 408
authorizes EPA to determine a residue
is safe and therefore exempt from the
requirement of a tolerance if the
Administrator ‘‘has determined that
there is a reasonable certainty that no
harm will result from aggregate
exposure to the pesticide chemical
residue, including all anticipated
dietary exposures and all other
exposures for which there is reliable
information’’ (21 U.S.C.
346a(c)(2)(A)(ii)). Section 408 of the
FFDCA also directs EPA to specifically
consider harm that may result to infants
and children as a result of pesticide
chemical residues. For additional
discussion of this standard, see the
Exemption from the Requirement of a
Tolerance under the Federal Food, Drug,
and Cosmetic Act for Residues of Plant
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Virus Coat Proteins that are Part of a
Plant-Incorporated Protectant published
concurrently in today’s Federal
Register.
EPA uses the FFDCA section 408
safety standard in evaluating whether a
pesticide used in food meets the FIFRA
section 25(b)(2) exemption standard
with respect to human dietary risk. A
pesticide in food poses a low probability
of human dietary risk if it meets the
FFDCA section 408 standard for an
exemption from the requirement of a
tolerance. Such a pesticide also is not
likely to cause unreasonable adverse
effects to the environment, with respect
to human dietary risk only, if the dietary
risks resulting from use of that pesticide
are consistent with the FFDCA section
408 exemption standard, and the
potential benefits of use outweigh any
dietary risk even in the absence of
regulatory oversight.
FIFRA, however, does not provide for
exemption of a pesticide in food based
solely upon human dietary risk and
consistency with the FFDCA section 408
exemption standard; an exemption from
the requirements of FFDCA does not
exempt a product from regulation under
FIFRA. For an exemption under FIFRA,
EPA must also evaluate non-dietary
risks to humans and the remainder of
the environment from the pesticide and
determine both that the pesticide poses
only a low probability of non-dietary
risks and that use of the pesticide is not
likely to cause any unreasonable
adverse effects to the environment from
such nondietary risks in the absence of
regulation.
D. What is the Role of Other Federal
Agencies?
EPA is the Federal agency responsible
for the regulation of pesticides. Under
the Coordinated Framework for
Regulation of Biotechnology (51 FR
23302, June 26, 1986), EPA works
closely with the U.S. Department of
Agriculture (USDA), which has
responsibilities under the Plant
Protection Act (PPA), and the U.S. Food
and Drug Administration (FDA), which
has responsibilities under FFDCA. EPA,
USDA, and FDA consult and exchange
information when such consultation is
helpful in resolving safety questions.
The three agencies also strive for
consistency between programs
following one of the basic tenets of the
Coordinated Framework, i.e., that the
agencies composing the Framework
adopt consistent approaches to the
extent permitted by the respective
statutory authorities. A consistent
approach between agencies is easier for
the regulated community to understand,
and it likely conserves resources
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because data developed for one agency
may meet at least some of the
requirements posed by another agency
for the same or similar products.
1. USDA. USDA has the responsibility
of preventing the introduction and
dissemination of plant pests under the
PPA. Before a genetically engineered
plant that is subject to the PPA may be
introduced into the environment,
approval must be obtained from the
USDA/Animal Plant Health Inspection
Service (APHIS) unless such a plant has
been reviewed and granted
Nonregulated Status. The USDA
regulations use genetic engineering and
potential plant pest risk as criteria for
determining the scope of its regulations
(62 FR 23945, May 2, 1997). Any
genetically engineered plant that
contains genetic material from a plant
pest is subject to the regulations. Thus,
all plants containing PVCP-PIPs are
subject to USDA/APHIS requirements
under the PPA.
EPA therefore recognizes that there is
a potential for duplicative oversight
with respect to certain issues that may
arise in decisions about PVCP-PIPs that
require any review by EPA. For
example, in its reviews of Petitions for
Determination of Nonregulated Status
under regulations at 7 CFR part 340, the
potential for weediness, for
displacement of native species, and
potential consequences of gene transfer
are evaluated by USDA/APHIS. EPA
and USDA/APHIS will continue to
consult and collaborate on reviews of
PVCP-PIPs. EPA and USDA/APHIS will
work together to avoid potential
duplication and inconsistencies and to
coordinate their analyses in accordance
with their respective expertise and
jurisdiction.
2. FDA. FDA is the primary U.S.
agency responsible for ensuring the
safety of commercial food and food
additives. FDA’s authority under
FFDCA extends to any nonpesticidal
substance that may be introduced into a
new plant variety and that is expected
to become a component of food.
Pursuant to sections 201 and 408 of
FFDCA and the creation of EPA,
pesticide chemical residues are subject
to EPA’s regulatory authority under
FFDCA.
E. What is a PVCP-PIP?
EPA is proposing to define a PVCPPIP as ‘‘a plant-incorporated protectant
derived from one or more genes that
encode a coat protein of a virus that
naturally infects plants. This includes
plant-incorporated protectants derived
from one or more plant viral coat
protein genes that produce only RNA
and no virus-related protein.’’
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Coat proteins are those substances
that viruses produce to encapsulate and
protect the viral nucleic acid and to
perform other important tasks for the
virus, e.g., assistance in viral
replication, movement within the plant,
and transmission of the virus from plant
to plant by insects (Ref. 1). In many
cases, when the genetic material
encoding a plant virus coat protein is
engineered into a plant’s genome, the
plant displays resistance to infection by
that virus as well as other viruses
having similar coat protein sequences
(Ref. 2).
Current scientific information
suggests that prevention or mitigation of
disease by PVCP-PIPs may occur by two
different mechanisms. For some PVCPPIPs, resistance is believed to be
protein-mediated because efficacy is
correlated with the concentration of coat
protein produced by the transgene (Ref.
3). In protein-mediated resistance, the
coat protein is thought to impede the
infection cycle by interfering with the
disassembly of infecting viruses (Ref. 4).
In transgenic plants, a second
mechanism of resistance, posttranscriptional gene silencing (PTGS)
may be activated. In PTGS, prevention
or mitigation of viral disease is not
correlated with the level of coat protein
expression. Indeed, virus resistance can
occur even when a coat protein gene
expresses untranslatable RNA sequences
and no coat protein is detected (Ref. 4).
PTGS is a defense mechanism in plants
against foreign RNA (e.g., viruses) in
which sequence-specific RNA
degradation is initiated by the plant in
response to the foreign RNA itself.
Evidence suggests that PTGS is initiated
once there is a threshold accumulation
of double-stranded (ds) RNA in the cell
cytoplasm (Ref. 5). Over 90% of plant
viruses have single-stranded RNA
genomes, but viral replication
transiently produces dsRNA in
quantities sufficient to trigger PTGS
(Ref. 6). PTGS is also known to occur
with transgenes that are transcribed at a
low level but that likely produce dsRNA
(Ref. 7). Once the plant recognizes the
dsRNA, it is thought to be cleaved by a
dsRNA-specific nuclease to produce
small 21- to 25-nucleotide short
interfering RNA sequences (siRNAs; Ref.
8). The siRNAs are thought to serve as
guides for the cleavage of singlestranded RNA with a sequence similar
to the dsRNAs (Ref. 9). Thus once PTGS
is initiated, it targets all RNA with high
sequence similarity to the sequence that
initiated the process, regardless of
whether it was transcribed from the
transgene, an endogenous gene, or viral
RNA.
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A plant virus coat protein transgene
that confers virus resistance through
either a protein- or RNA-mediated
mechanism would fall within EPA’s
proposed definition of a PVCP-PIP. The
substances involved in either
mechanism of resistance would meet
the FIFRA definition of a pesticide
because the transgene and any material
expressed from the transgene are
introduced into a plant for the purpose
of preventing or mitigating viral disease
(see Unit II.A.).
The proposed definition of a PVCPPIP contains the phrase ‘‘naturally
infects plants.’’ Including this phrase in
the definition would specifically limit
the proposed exemption by requiring
that the virus coat protein gene
sequence used in the PVCP-PIP be based
exclusively on a plant virus sequence.
This limitation is proposed in order to
exclude from the definition any coat
proteins of plant viruses that have been
modified with sequences from animal or
human viruses. EPA includes this
concept in today’s proposal in response
to comment received from the public in
earlier Federal Register documents
pertaining to PVCP-PIPs.
F. What Conditions Must be Met for a
PVCP-PIP to Qualify for a FIFRA
Exemption?
As noted above, a PIP is exempt from
the requirements of FIFRA, other than
the adverse effects reporting
requirements of 40 CFR 174.71, if the
PIP meets the requirements in 40 CFR
174.21(a), (b), and (c). Therefore, the
following factors need to be considered
to determine the FIFRA status of a
PVCP-PIP. First, does the PVCP-PIP
meet the requirement at 40 CFR
174.21(a)? Second, do the residues of
the PVCP-PIP meet the requirement at
40 CFR 174.21(b)? Third, do the inert
ingredients that are part of the PVCP-PIP
meet the requirement at 40 CFR
174.21(c)?
1. Does the PVCP-PIP meet the
requirement at 40 CFR 174.21(a)?
Section 174.21(a) requires that the PIP
meet the criteria listed in at least one of
the sections in §§ 174.25 through
174.50. Today’s action proposes to
establish § 174.27, which would contain
criteria allowing certain PVCP-PIPs to
meet the § 174.21(a) requirement for
exemption. These criteria identify those
PVCP-PIPs that EPA has been able to
determine meet the standard under
FIFRA section 25(b)(2), i.e., that pose a
low probability of risk to the
environment and that are not likely to
cause unreasonable adverse effects to
the environment even in the absence of
regulatory oversight under FIFRA. EPA
is proposing criteria that address the
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relevant potential risks associated with
these products:
i. The potential for increased
weediness or invasiveness of the crop
plant containing the PVCP-PIP or any
wild or weedy relatives that could
acquire the PVCP-PIP through gene flow
thereby causing negative effects on
either the agro-ecosystem or natural
environments. This issue is addressed at
§ 174.27(a) and is referred to as
‘‘weediness’’ for the purposes of this
document.
ii. The potential for viruses with
novel properties developing through
novel viral interactions. This issue is
addressed at § 174.27(b) and is referred
to as ‘‘viral interactions’’ for the
purposes of this document.
iii. The potential for human or
nontarget organism exposure to proteins
that may not have previously existed in
nature and thus should be examined to
determine whether they have
potentially toxic or allergenic
properties. This issue is addressed at
§ 174.27(c) and is referred to as ‘‘protein
production’’ for the purposes of this
document.
Proposed §§ 174.27(a), (b), and (c) are
discussed in greater detail in Unit III of
this Federal Register document. In
addition, a graphical depiction of what
this rule is proposing is available in the
docket for this proposed rule.
2. Do the residues of the PVCP-PIP
meet the requirement at 40 CFR
174.21(b)? Section 174.21(b) requires
that in order to qualify for a FIFRA
exemption, the residues of a PVCP-PIP
that is intended to be produced and
used in a crop used as food must either
be exempted from the requirement of a
tolerance under FFDCA or no tolerance
would otherwise be required for the
PVCP-PIP. Therefore, if a PVCP-PIP is
used in a food plant (e.g., the PVCP-PIP
is produced and used in a corn plant)
or residues of the PVCP-PIP might
reasonably be expected in food (e.g., the
PVCP-PIP is produced and used in an
ornamental plant but could move
through gene flow to a sexually
compatible food plant), the FFDCA
section 408 requirements must be
considered when determining whether
the PVCP-PIP can be exempted under
FIFRA. If a PVCP-PIP would not be used
in and would not reasonably be
expected in a crop used as food (e.g., the
PVCP-PIP is produced and used in an
ornamental plant with no sexually
compatible relatives that are food
plants), the FFDCA section 408
requirements do not need to be
considered.
EPA anticipates that in most cases the
PVCP-PIP residues will consist of
residues of nucleic acids, residues of
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inert ingredients, and residues of the
plant virus coat protein portion of the
PVCP-PIP (the ‘‘PVC-protein’’). Residues
of nucleic acids are exempt from the
requirement of a tolerance at 40 CFR
174.475. As of the time this proposed
rule is being issued, residues of those
inert ingredients that are exempt from
the requirement of a tolerance are listed
at 40 CFR part 180 and 40 CFR part 174
subpart W. In a companion piece
appearing in today’s Federal Register,
EPA is proposing a tolerance exemption
for residues of certain PVC-proteins that
meet specified criteria. Due to different
statutory requirements, the proposed
FFDCA exemption criteria differ from
the criteria proposed in this Federal
Register for 40 CFR 174.27 under
FIFRA.
3. Do the inert ingredients that are
part of the PVCP-PIP meet the
requirement at 40 CFR 174.21(c)?
Section 174.21(c) requires that in order
for a PIP to qualify for exemption any
inert ingredient contained in the PIP
must be codified at subpart X of 40 CFR
part 174 - List of Approved Inert
Ingredients. Subpart X lists the inert
ingredients (i) that may be used in a
plant-incorporated protectant listed in
subpart B (Exemptions) of part 174 and
(ii) whose residues are either exempted
from the requirement of a tolerance
under FFDCA or no tolerance would
otherwise be required. EPA is proposing
to add several substances known to be
used commonly as inert ingredients in
PIPs to 40 CFR part 174 subpart X.
These substances already have tolerance
exemptions under FFDCA. EPA
proposes in today’s Federal Register
that these substances, when used in
exempt PIPs as inert ingredients under
specified conditions, should also be
exempt from FIFRA because they are of
a character which is unnecessary to be
subject to FIFRA in order to carry out
the purposes of the Act.
G. What if a PVCP-PIP Does Not Qualify
for Exemption?
If EPA is unable to conclude that a
PVCP-PIP meets the standard for
exemption, an applicant may still apply
to register the PVCP-PIP under section
3 of FIFRA. EPA may be able to
conclude that the PVCP-PIP meets the
standard for registration (i.e., when it is
used in accordance with widespread
and commonly recognized practice, it
will not generally cause unreasonable
adverse effects on the environment).
EPA recognizes that the proposed
exemption criteria may not identify all
low risk PVCP-PIPs. A case-by-case
review for registration would allow the
Agency to evaluate factors not readily
incorporated into clear, unambiguous
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exemption criteria. As part of
registration, the Agency could also
impose conditions of use as appropriate.
As is EPA’s general practice regarding
registration of PIPs, the Agency will
consult with USDA in evaluating PVCPPIPs for registration.
H. What is the History of this Proposal?
1. Scientific input. EPA sponsored or
cosponsored with other Federal
agencies, six conferences relevant to
development of this proposed rule: on
October 19–21, 1987, a meeting on
‘‘Regulatory Considerations: Genetically
Engineered Plants’’ at Cornell
University in Ithaca, New York; on
September 8–9, 1988, a ‘‘Transgenic
Plant Conference’’ in Annapolis,
Maryland; on November 6–7, 1990, a
conference on ‘‘Pesticidal Transgenic
Plants: Product Development, Risk
Assessment, and Data Needs’’ in
Annapolis, Maryland; on April 18–19,
1994, a ‘‘Conference on Scientific Issues
Related to Potential Allergenicity in
Transgenic Food Crops’’ in Annapolis,
Maryland; on July 17–18, 1997, a ‘‘Plant
Pesticide Workshop’’ in Washington,
DC; and on December 10–12, 2001 a
conference on ‘‘Assessment of the
Allergenic Potential of Genetically
Modified Foods’’ in Chapel Hill, North
Carolina. EPA incorporated information
from these conferences in development
of this proposed rule as appropriate.
EPA has requested the advice of two
scientific advisory bodies at five
meetings while developing its approach
to plant-incorporated protectants. On
December 18, 1992, EPA convened a
FIFRA Scientific Advisory Panel (SAP)
to review a draft policy on PIPs (then
called plant-pesticides) and to respond
to a series of related questions posed by
the Agency dealing primarily with
EPA’s approach under FIFRA. On July
13, 1993, EPA requested the advice of a
Subcommittee of the EPA Biotechnology
Science Advisory Committee (BSAC) on
a series of scientific questions dealing
with EPA’s approach to PIPs under
FFDCA. On January 21, 1994, EPA
asked for advice on the Agency’s
approach to PIPs under both statutes at
a joint meeting of the SAP and the
BSAC. To evaluate more recent
scientific advances, EPA again brought
these issues to a FIFRA SAP meeting on
October 13–14, 2004. On December 6–
8, 2005, EPA convened a SAP meeting
to address a series of scientific questions
related to this proposal. EPA
incorporated advice from all five
meetings in development of this
proposed rule as appropriate.
2. Federal Register documents. The
history of this proposal consists of the
original proposed exemption from
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FIFRA requirements that appeared in
the November 23, 1994 Federal Register
(59 FR 60519); the original proposed
exemption from FFDCA tolerance
requirements in the November 23, 1994
Federal Register (59 FR 60545); and
several supplemental documents
appearing in the May 16, 1997 Federal
Register (59 FR 27149), the July 22,
1996 Federal Register (61 FR 37891),
the April 23, 1999 Federal Register (64
FR 19958), and the July 19, 2001
Federal Register (66 FR 37772 and
37855).
i. November 23, 1994. In a document
that appeared in the November 23, 1994
Federal Register (59 FR 60519) (FRL–
4755–3), EPA proposed two alternatives
under FIFRA section 25(b)(2) to exempt
PVCP-PIPs from FIFRA requirements.
Option 1 proposed to categorically
exempt plant-pesticides derived from
coat proteins from plant viruses (now
called PVCP-PIPs). Option 2 proposed a
more limited exemption covering only
those PVCP-PIPs that would have the
least potential to confer selective
advantage on free-living wild relatives
of the plants that could acquire the
PVCP-PIP through gene flow (discussed
in detail in Unit III.C.3.).
Elsewhere in the November 23, 1994,
Federal Register (59 FR 60545) (FRL–
4755–4), EPA proposed to exempt from
the FFDCA requirement of a tolerance,
residues of plant virus coat proteins
produced and used in living plants as a
plant-incorporated protectant (then
called a plant-pesticide). The proposed
exemption from the requirement of a
tolerance read, ‘‘Residues of coat
proteins from plant viruses, or segments
of the coat proteins, produced in living
plants as plant-pesticides are exempt
from the requirement of a tolerance’’ (59
FR 60547).
ii. May 16, 1997. In August of 1996,
Congress enacted the Food Quality
Protection Act (FQPA), which amended
FFDCA and FIFRA. On May 16, 1997,
EPA published a supplemental
document in the Federal Register (62
FR 27149) (FRL–5716–6) to provide the
public with an opportunity to comment
on EPA’s analysis of how certain FQPA
amendments to FFDCA and FIFRA
applied to the 1994 proposed exemption
from the requirement of a tolerance for
residues of viral coat proteins produced
in plants as part of a PIP. (Today’s
Federal Register terms such entities
‘‘PVC-proteins.’’)
In the 1997 supplemental document,
EPA explained how most of the
substantive factors that the amended
FFDCA requires EPA to consider in
evaluating pesticide chemical residues
had been considered in the Agency’s
1994 proposed tolerance exemption.
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Even though the Agency may not have
used the terminology specified in the
FQPA, EPA did take into account most
of the factors (e.g., toxicity and
consumption patterns) in issuing its
1994 proposal to exempt residues of
PVC-proteins, or residues of segments of
such proteins, from FFDCA tolerance
requirements. EPA therefore sought
comment on the requirements imposed
by FQPA that the Agency had not
addressed in its 1994 proposal,
specifically:
a. EPA’s conclusion that there are no
substances outside of the food supply
that may have a cumulative toxic effect
with residues of PVC-proteins,
b. EPA’s conclusion that there are no
substances outside of the food supply to
which humans might be exposed
through non-occupational routes of
exposure that are related via a common
mechanism of toxicity to residues of
PVC-proteins,
c. Any available information on PVCproteins causing estrogenic effects,
d. EPA’s rationale, described in
greater detail, for concluding that PIPs
are likely to present a limited exposure
of pesticidal substances to humans in
which the predominant route of
exposure will be dietary, and
e. EPA’s rationale, described in
greater detail, for concluding that the
Agency’s analysis concerning the
dietary safety of food containing PVCproteins applies to infants and children
as well as adults.
Because of the 1996 FQPA, EPA’s
final determination under FIFRA for
PVCP-PIPs in food plants could also be
affected by comments on the companion
document in today’s Federal Register
that proposes a tolerance exemption for
certain PVCP-PIP residues.
iii. July 22, 1996. On July 22, 1996,
EPA issued a supplemental document
(61 FR 37891) (FRL–5387–4) requesting
comment on one aspect of its November
23, 1994 Federal Register document:
how the concept of inert ingredient
related to plant-incorporated
protectants.
iv. April 23, 1999. On April 23, 1999,
EPA published a supplemental
document in the Federal Register (64
FR 19958) (FRL–6077–6) soliciting
comment on whether to change the
name of pesticides produced and used
in living plants.
v. July 19, 2001. In July of 2001, EPA
published a package of notices related to
PIPs in the Federal Register, including
a supplemental document (66 FR 37855)
(FRL–6760–4) that provided the public
with additional opportunity to comment
on the FIFRA and FFDCA exemptions
for PIPs that the Agency proposed in
1994 but had not yet finalized by 2001.
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19595
EPA also requested comment on the
information, analyses, and conclusions
pertaining to these PIPs (including
PVCP-PIPs) contained in the NRC report
entitled ‘‘Genetically Modified PestProtected Plants: Science and
Regulation’’ (Ref. 10). The public was
given an opportunity to comment on a
proposal to clarify the language of the
original 1994 proposals EPA was
considering in response to public
comment received on the 1994 proposal.
In addition, the Agency requested
additional public comment on several
scientific issues. Also in the July 19,
2001 Federal Register (66 FR 37772)
(FRL–6057–7), EPA changed the name
of these pesticides from ‘‘plantpesticides’’ to ‘‘plant-incorporated
protectants’’ or ‘‘PIPs.’’
The documents and reports of the
meetings described above, including
associated public comments, are
available in the public dockets
established for the associated
rulemakings as described in Unit IX of
this preamble.
Today’s proposed rule completely
supersedes these previous proposals.
EPA does not intend to respond to
comments submitted on those
proposals. Thus, individuals who
believe that any comments submitted on
any of the earlier proposals remain
germane to today’s proposal, should
submit them (or relevant portions) again
during this comment period.
III. Proposed Exemption Criteria under
§ 174.27
A. Structure of the Proposed Exemption
Criteria under § 174.27
In order to satisfy the general
requirement for a FIFRA exemption
listed at 40 CFR 174.21(a), EPA is
proposing to add three criteria at 40 CFR
174.27. As discussed in Unit II.F.1., the
three criteria that EPA is proposing to
adopt at 40 CFR 174.27 are intended to
address three issues that are associated
with potential risks of PVCP-PIPs.
The PVCP-PIP would have to meet
proposed §§ 174.27(a), (b), and (c) to
satisfy 40 CFR 174.21(a). Proposed
§§ 174.27(a), (b), and (c) each can be met
in one of two ways: a product developer
may self-determine that paragraph (1) of
the criterion is met (i.e., § 174.27(a)(1),
(b)(1), or (c)(1)) or the Agency may
determine that paragraph (2) of the
criterion is met (i.e., § 174.27(a)(2),
(b)(2), or (c)(2), respectively). Paragraph
(1) of each proposed criterion (i.e.,
§ 174.27(a)(1), (b)(1), and (c)(1))
describes an objective, well-defined
characteristic. Therefore, the developer
may determine whether the PVCP-PIP
meets the requirement. Paragraph (2) of
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each proposed criterion (i.e.,
§ 174.27(a)(2), (b)(2), and (c)(2)) is
conditioned on an Agency
determination because several types of
information may need to be evaluated
using a weight-of-evidence approach to
determine whether the PVCP-PIP meets
the requirement and is therefore of a
nature warranting exemption.
1. Exemption by self-determination.
Each criterion may be satisfied under
either paragraph (1) or paragraph (2)
irrespective of how the other two
criteria are satisfied; there is no
requirement that all three criteria must
be satisfied under either paragraph (1)
or paragraph (2) in order for a PVCP-PIP
to qualify for the exemption. However,
if a PVCP-PIP satisfies all three criteria
under paragraph (1) by developer self
determination (i.e., it meets proposed
§§ 174.27(a)(1), (b)(1), and (c)(1)) and it
satisfies §§ 174.21(b) and (c), EPA is
proposing that the developer submit a
notification to the Agency of that
determination and certify that the
PVCP-PIP qualifies for exemption under
FIFRA, i.e., that the PVCP-PIP meets
§§ 174.21(a), (b), and (c). In addition,
EPA is proposing that the developer
maintain information adequate to
support the determination. Such records
must be made available for EPA
inspection and copying or be otherwise
submitted to the Agency for review
upon request for the duration of time
that the PVCP-PIP is sold or distributed.
EPA is proposing that these records be
kept so that EPA could review a
particular exemption determination if
needed at a future date.
EPA is proposing to require that the
notifications contain:
i. The name of the crop (including
genus and species) containing the
PVCP-PIP.
ii. The name of the virus from which
the coat protein gene was derived.
iii. The name of the virus(es) to which
resistance is conferred.
iv. When available, a unique
identifier.
EPA is proposing this notification
requirement because it provides a
mechanism that allows the Agency to
keep a record of all PVCP-PIPs that may
be sold or distributed. EPA expects that
such a list would be useful to
developers whose products are moving
in international trade because it would
enable EPA to post information on the
United States Regulatory Agencies
Unified Biotechnology Website (found
at https://usbiotechreg.nbii.gov/database
_pub.asp) indicating that the developer
has determined that the product
satisfies the Agency’s safety
requirements. Such information can
facilitate acceptance by importing
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countries. Absent such a posting, the
field for EPA information would be
blank, and importers might question the
regulatory status of the product in the
United States. In addition, EPA
considers that such a list may be useful
to the Agency for ensuring enforcement
and compliance with FIFRA regulations
because it will enable compliance
personnel to ascertain the exemption
status of products encountered in
distribution and trade channels.
2. Exemption by Agency
determination. If a PVCP-PIP does not
satisfy a particular criterion under
paragraph (1) (i.e., § 174.27(a)(1), (b)(1),
or (c)(1)), EPA proposes that as an
alternative route to exemption, the
product developer would submit data or
other information to the Agency to
demonstrate that a particular PVCP-PIP
meets paragraph (2) of that criterion
(i.e., it meets § 174.27(a)(2), (b)(2), or
(c)(2), respectively). In addition, as part
of this submission, a developer would
also include a certification as to any
determination that the product meets
§ 174.27(a)(1), (b)(1), and/or (c)(1), as
appropriate. During its review under
§ 174.27(a)(2), (b)(2), and/or (c)(2), EPA
would not review the developer’s
determination that the product met any
criterion under § 174.27(a)(1), (b)(1), or
(c)(1).
EPA expects that in many instances
developers would have most, if not all
the information that would need to be
included in any exemption submission
under §§ 174.27(a)(2), (b)(2), or (c)(2)
because it would have been gathered in
the course of product development or
for submission to USDA/APHIS as part
of a petition for determination for nonregulated status. EPA will consult with
USDA in evaluating whether a PVCPPIP meets the conditions for an Agencydetermined exemption. EPA is
proposing that information supporting
the submission be maintained as records
that will be available for EPA inspection
as necessary for the duration of time
that the PVCP-PIP is sold or distributed.
EPA will evaluate the information
contained in the submission and
publish a notice allowing the public to
comment on the Agency’s determination
that a product meets § 174.27(a)(2),
(b)(2), and/or (c)(2), as appropriate. EPA
is providing such a public comment
period because even though the public
will have had the opportunity to
comment through this proposal on the
appropriateness of the criteria in
§ 174.27(a)(2), (b)(2), and (c)(2), the
public would not otherwise have an
opportunity to comment on whether a
particular PVCP-PIP meets these
criteria, given that these determinations
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depend on a case-by-case analysis of
several types of information.
The Agency plans to publish a
Federal Register notice announcing its
determination that a PVCP-PIP meets
§ 174.27(a)(2), (b)(2), and/or (c)(2), and if
no adverse comments are received
during the comment period, the
Agency’s decision will be considered
final, and EPA will publish no further
notice. Based on its experience with
EUP notices, EPA expects that, in
general, determinations that a PVCP-PIP
qualifies for exemption will be
noncontroversial and generate no
adverse comments. However, in the case
of adverse comments, EPA would
publish a subsequent Federal Register
notice announcing its final
determination and address all public
comments. EPA would prefer criteria in
§ 174.27(a)(2), (b)(2), and (c)(2) that
would allow the public and PVCP-PIP
developers to readily predict the
outcome of an Agency review. Such
criteria would reduce regulatory
uncertainty in PVCP-PIP development
and decrease the time EPA would need
to evaluate the data/information
necessary to make a determination that
a PVCP-PIP meets a given criterion.
However, using criteria for which
determinations can be readily predicted
might reduce the number of PVCP-PIPs
that would qualify for exemption. EPA
tried to balance these concerns and
proposed multiple options when the
Agency was unsure how to resolve this
dilemma.
However, EPA does not believe that
the considerations underlying its
decisions to grant the public a further
opportunity to comment on the
Agency’s decision apply in cases where
the Agency rejects a submission for an
exemption. Accordingly, if EPA
determines that the product fails to meet
one or more of the exemption criteria,
EPA will provide notice to the applicant
of its decision on the submission and
that a registration would be required for
the PVCP-PIP before the PVCP-PIP
could be sold or distributed. The
product developer may then submit an
application for registration to the
Agency. EPA would evaluate such
PVCP-PIPs under the existing
registration process and could
implement conditions of use as
appropriate.
B. Key Scientific Issues Associated with
the Proposed Exemption Criteria under
§ 174.27
Several scientific questions
concerning risk issues associated with
PVCP-PIPs have been identified:
• What is the potential for a PVCPPIP to endow plants with characteristics
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that could disrupt the existing network
of ecological relationships in managed,
semi-managed, or natural ecosystems,
e.g., through gene transfer to wild or
weedy1 relatives? This issue is
addressed at proposed § 174.27(a) and is
referred to as ‘‘weediness’’ for the
purposes of this discussion.
• What is the potential for
interactions between a PVCP-PIP and an
infecting virus to affect plant virus
epidemiology or pathogenicity? This
issue is addressed at proposed
§ 174.27(b) and is referred to as ‘‘viral
interactions’’ for the purposes of this
discussion.
• What is the potential for exposure
of humans or nontarget organisms to
PVC-proteins with novel toxic or
allergenic properties? This issue is
addressed at proposed § 174.27(c) and is
referred to as ‘‘protein production’’ for
the purposes of this discussion.
These three questions are addressed
below under the headings of weediness,
viral interactions, and protein
production, respectively.
C. Weediness
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1. Scientific issues. In evaluating
whether a PVCP-PIP could alter
ecological relationships among plants,
EPA considered two primary issues: (1)
whether the PVCP-PIP could endow a
transgenic plant itself with an increased
ability to spread into natural or semimanaged habitats and (2) whether the
transfer of a PVCP-PIP from a transgenic
plant into wild or weedy relatives could
endow the wild or weedy relative with
increased competitive ability and thus
disrupt ecological relationships. Gene
transfer among sexually compatible
plants is a natural phenomenon that
EPA does not consider to be an
environmental risk per se. Whether the
transfer of a PVCP-PIP could
significantly disrupt ecological
relationships in specific instances
depends on all of the following
considerations: First, does the crop
plant containing the PVCP-PIP have
wild relatives with which it is able to
hybridize in nature? If it does not, there
can be no gene transfer. Second, if there
are sexually compatible relatives, is the
1 In the context of the phrase ‘‘wild and weedy’’
relatives/plants used throughout this preamble,
EPA considers weedy plants to be those with the
characteristics of weeds, i.e., those that are
considered undesirable, unattractive, or
troublesome, especially when growing where they
are not wanted. Wild plants are those that occur,
grow, and live in a natural state and are not
domesticated, cultivated, or tamed. EPA considers
a naturalized population to be an enduring
population of domesticated plants that grows in
wild (non-cultivated) areas. EPA considers a native
plant population to be one that originates in a
particular region or ecosystem.
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gene conferring virus resistance likely to
become stable in the population? Third,
is the stable introduction of a PVCP-PIP
into the plant population (i.e.,
introgression) likely to cause the
population to become more weedy/
invasive or otherwise alter its
competitive ability, thereby significantly
changing the population dynamics of
the plant community? The 2005 SAP
concurred that these are important
considerations for PVCP-PIPs by noting
that an ‘‘important ecological risk
associated with gene flow from crop
plants into their wild relatives is that
the acquisition of crop genes might
substantially alter the population
dynamics of the wild plant. In
particular, a transgene introgressed from
the crop relative into a wild population
might allow the wild species to persist
in larger populations across a larger
geographic range, or in a wider range of
habitats. Collectively these changes in
population dynamics can be considered
‘increased weediness’. The probability
that a particular transgene will lead to
increased weediness depends on the
phenotype conferred by the transgene
and on the ecological factor(s) currently
limiting the size or distribution of the
wild species. In particular, if the
transgene alters plant response to the
ecological factor limiting population
size, then population dynamics may be
affected. For PVCP-PIPs, the relevant
consideration is whether virus
resistance (conferred by the PVCP-PIP)
leads to changes in the size or
distribution of wild plant species with
the PVCP-PIP’’ (Ref. 11).
i. Likelihood that a crop plant
containing a PVCP-PIP could itself
disrupt ecological relationships. In
considering whether a PVCP-PIP could
affect the ability of a plant to spread into
natural or semi-managed habitat at the
margins of cultivated fields, i.e., to form
feral or naturalized populations, the key
consideration is whether viral infection
is currently limiting the ability of
agricultural crops to do so. The 2005
SAP pointed out that PVCP-PIPs ‘‘are
developed when virus infection of a
crop reduces the crop yield, suggesting
that virus infection is quite likely in
naturalized populations of the crop as
well’’ (Ref. 11). However, virus infection
in crop plants does not necessarily limit
the spread of the crop into natural or
semi-managed areas. As the 2005 Panel
also noted, ‘‘little is known about factors
controlling population size in plant
populations in general, including those
that are currently stable, as well as those
that are currently weedy or invasive’’
(Ref. 11). Few published studies are
available that evaluate this question
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directly, perhaps due to the general
rarity of negative results in scientific
literature. However, one study did find
virus infection to have little effect on an
agricultural crop. Field experiments
with transgenic virus-resistant sugar
beets revealed no competitive advantage
(measured as seedling emergence and
biomass production) between the
transgenic and susceptible control lines
(Ref. 12).
Although virus infection has been
shown to negatively impact growth and/
or reproduction of some natural plant
communities (discussed below in Unit
III.C.1.ii.), EPA recognizes that there is
reason to question whether the situation
would be different for crop plants. The
National Research Council (NRC) noted
in 1989 that most naturalized,
domesticated crops generally are unable
to effectively compete with wild species
in natural ecosystems and have not been
known to acquire this ability with the
type of single-gene traits commonly
introduced through genetic modification
(Ref. 13). The 1989 NRC report went on
to note that plant breeders have
capitalized for decades on the fact that
relatively minor genetic changes can
produce plants with altered ecological
properties, but the addition of pest
resistant traits has not been known to
result in increased weediness of widely
used crops (Ref. 13). A 1989 survey of
the weedy characteristics of crop versus
weed species showed that weeds
possess significantly more weedy
characteristics on average than do crop
plants (Ref. 14). For domesticated crops,
the traits that make them useful to
humans also reduce their competitive
ability in nonagricultural habitats. Crops
that have been subjected to long-term
breeding (e.g., corn and soybeans) are
unlikely to possess characteristics that
would allow the plant to compete
effectively outside of managed
ecosystems. Domesticity arises because
intensive breeding efforts seek to
eliminate many characteristics of the
crop plant that would enhance
weediness (e.g., seed shattering, thorns,
seed dormancy, and bitterness). For
example, lack of seed shattering and
seed dormancy greatly reduces the
ability of an annual crop to persist
without human intervention. Highly
domesticated crops such as corn are
thus unlikely to survive for multiple
generations outside agricultural fields
no matter what transgenic trait they
contain, including virus resistance (Ref.
15).
However, some crop species, e.g.,
cranberry and blackberry may have
more similarities to their wild relatives
than highly domesticated crops such as
corn or soybean. As noted by the 2005
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SAP, ‘‘Determining whether a particular
crop can naturalize and then spread as
a weedy species is difficult to ascertain
from the literature and determining the
probability that a crop will be more
weedy or invasive if it contains a PVCPPIP is even more difficult’’ (Ref. 11).
Such determinations may therefore need
to rely on information not available in
public literature as part of a risk
assessment for a particular plant. Plants,
such as forest trees, that may grow for
many years in natural environments or
in very close proximity to natural
environments present additional
difficulty in evaluating and managing
risks (Ref. 16). The period of time over
which such plants would persist is
significantly longer than for annual,
short-lived species. Individual plants
will therefore experience a much wider
range and variety of stress conditions,
enemy attacks, and climate change,
making predictions about naturalization
potential with acquired virus resistance
particularly challenging.
Thus, although EPA believes that
many crop species are unlikely to
disrupt ecological relationships through
acquisition of a PVCP-PIP, the available
information is insufficient to support
the general conclusions that EPA would
need to make for a categorical
exemption of PVCP-PIPs. EPA would
need to conclude that there is a low risk
that acquisition of a PVCP-PIP would
significantly affect the competitiveness
of any of the plants currently grown as
crops and that none of these crop
species would significantly disrupt
ecological relationships when modified
to contain a PVCP-PIP. Therefore, the
Agency believes that it is necessary to
evaluate each plant species
independently to consider whether it is
likely to establish weedy or invasive
populations outside of agricultural
fields in the United States and thereby
potentially significantly disrupt
ecological relationships if it becomes
virus resistant due to a PVCP-PIP.
Factors likely to influence this
determination cannot be readily
distilled into a straightforward criterion
suitable for a categorical exemption.
ii. Likelihood that a crop plant
containing a PVCP-PIP could
significantly disrupt ecological
relationships through gene transfer. The
question of whether gene transfer from
a crop to a wild or weedy relative could
significantly disrupt ecological
relationships is a more complicated
question because a much broader range
of potential plants may be involved
when wild or weedy relatives are
considered in addition to the crops
themselves. The answer to this question
depends first on the question of whether
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the transgenic crop plants could transfer
a PVCP-PIP to other plant populations.
This potential for transfer depends in
part on the frequency of hybridization
between domesticated species and their
wild relatives. Hybridization is affected
by the ability of plants to cross-pollinate
which in turn is affected by their timing
of reproductive viability and the
proximity of the plants. Hybridization is
also affected by the ability of pollen to
fertilize recipient plants, the recipient
plants to develop viable seeds, these
seeds to germinate, and the seedlings to
grow into viable adults (Ref. 17). In spite
of these potential constraints, a survey
of the world’s most important crops
suggests that spontaneous hybridization
of domesticated plants with wild
relatives appears to be a general feature
across at least a portion of the
worldwide geographic area over which
each is cultivated (Refs. 18 and 19). The
ability to cross crops with wild relatives
(which may not necessarily occur where
the crop is grown) is also the basis of
many traditional breeding techniques
that are used for virtually all crops (Ref.
20).
Whether virus infection limits the
growth and/or reproductive ability of
wild or weedy plant populations is
more difficult to answer generically for
all plants in all ecosystems. Viruses are
pervasive in many natural plant
populations (Refs. 21, 22, 23, and 24),
although a comprehensive body of
literature on the effect of viruses in
weed species is lacking. According to
the 2004 SAP, ‘‘Our knowledge about
the effect of virus infection on non-crop
plants is quite limited’’ (Ref. 25). Some
published studies report that virus
infection can have little or no effect on
the plants. For example, a survey of
Plantago species in England showed
that although 92 of 144 plants were
infected with one or more viruses, most
of the plants showed no obvious disease
symptoms (Ref. 23). A literature review
of the role of weeds in the occurrence
and spread of plant virus diseases
describes several cases where viruses
significantly damage certain crops but
have little effect on their weed hosts
(Ref. 26).
Other published studies have reported
that infection reduces plant growth and/
or fecundity. For example, naturally
occurring tobacco leaf curl virus
infection increases mortality and has
negative effects on growth and seed
output in plants from wild populations
of the flowering perennial plant
Eupatorium chinense (Ref. 27).
Greenhouse experiments with this same
plant under two irradiance levels
showed that virus infection did not
affect survivorship under high-light
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conditions but caused severe damage
under low-light conditions (Ref. 28).
Vegetative growth and flower
production of purslane (Portulaca
oleracea) was also reduced when plants
were inoculated with cucumber mosaic
virus (Ref. 29). Field experiments
showed that wild cabbage plants
(Brassica oleracea) inoculated with
turnip mosaic virus or turnip yellow
mosaic virus have reduced survival,
growth, and reproduction (Ref. 30).
Such experiments suggest that viruses
can sometimes reduce individual plant
growth and/or fecundity when infection
occurs. However, individual-level
effects are insufficient to understand
population-level processes. For
example, even if virus disease
significantly affected individual plant
fitness, a decline in individual-plant
fitness might reduce competition such
that uninfected plants could increase
reproductive output, thereby mitigating
any population-level effects (Ref. 31).
It can be difficult to predict the actual
impact on overall plant population
dynamics that would result from
acquisition of virus resistance by plants
that are in some way negatively affected
by virus infection. EPA is not aware of
any published study that has directly
examined this question by, for example,
purposefully freeing a plant species
from virus infection and investigating
the resulting population dynamics of
infected versus uninfected plants. The
2004 SAP was also unaware of any such
study, but offered that ‘‘[b]ased on
knowledge obtained from observation of
cultivated crops in the agroecosystem,
the majority of the Panel concluded that
it would be unlikely that a plant
population freed from viral pressure
would give a plant species a competitive
advantage’’ (Ref. 25). Some members of
the 2005 SAP agreed with the 2004 SAP,
while ‘‘[o]ther members of the current
[2005] SAP believed, based on new
information (Fuchs et al. 2004; Sukopp
et al., 2005) not available to the 2004
Panel, as well as EPA indicating a lack
of data on this topic, that concluding
that viruses typically have no effect on
their wild plant hosts is not accurate.
Because of the differing opinions among
the current [2005] Panelists, and the
general paucity of data, the Panel
cautioned that further research is
needed to provide stronger support to
this particular issue’’ (Refs. 11, 32, and
33). EPA also notes that evaluating
impacts on plant population dynamics
is further complicated because in
certain cases gene transfer of a PVCPPIP to wild or weedy relatives might
potentially be desirable. For example,
an invasive virus species might be
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effectively controlled through broad
acquisition of resistance by plant
species susceptible to the virus.
Controlling disease outbreaks in
perennial agricultural plants and trees
could be significantly aided by reducing
viral load in the environment through
such approaches.
A few studies are available that are
relevant to the question of whether
acquisition of virus resistance could
affect plant population dynamics. These
studies show that in some cases virus
infection can have such effects,
suggesting that acquired virus resistance
might as well. For example, infection
with alfalfa mosaic virus substantially
diminished the ability of certain medic
cultivars to compete with other species
such as capeweed in grazed pasture
swards, both directly by decreasing the
competitive ability of infected plants,
and indirectly by altering the
proportions in which the species
germinated (Ref. 34). In another
example of virus infection affecting
plant population dynamics, growth
analysis of Eupatorium makinoi
revealed that plants naturally infected
with a geminivirus had significantly
reduced stem growth and plant height,
along with decreased flowering and
survivorship. This study suggests that in
spite of the long-term coexistence of the
virus and Eupatorium makinoi, such
negative fitness attributes have a
significant impact on at least some local
plant populations in this species (Ref.
35).
Although relatively little research has
been published regarding how plant
population dynamics are directly
influenced by virus infection, such
results as described in the previous
paragraph provide some support for the
premise that virus resistance might be
an important ecological fitness
characteristic. At least some plant
populations acquiring virus resistance
might in some instances be able to better
compete against other species (Ref. 36)
and/or spread to habitats previously
unsuitable because of the presence of
the virus (Ref. 37). For example, a broad
survey of geographic data on plant
associations with viruses from
published compendia and governmental
or academic databases showed that
plants were infected by 24% fewer
viruses in their naturalized ranges than
in their native ranges, supporting the
hypothesis that the impact of invasive
plants results in part from reduced
natural enemy (e.g., virus) attack (Ref.
38). On the other hand, enemy release
is only one of many hypotheses that
could explain the abundance and/or
impact of an invasive plant (Ref. 39). In
addition, a few published studies have
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reported that in certain instances virus
infection can increase plant fitness,
suggesting that acquisition of virus
resistance might decrease plant fitness.
For example, infection by barley yellow
dwarf virus was found in at least 1 year
to increase the fitness of the host plant
green foxtail (Setaria viridis) by
approximately 25% (Ref. 40). In some
cases, plants might be more attractive to
herbivores when not infected by viruses,
as was found to be the case for dusky
coral pea (Kennedya rubicunda; Ref.
41). In this experiment, caged rabbits
presented with a mixture of carrots and
powdered plant extract grazed the
mixture made from virus-free plant
material at twice the rate as plant
material infected with Kennedya yellow
dwarf virus due presumably to greater
palatability. In general, negative fitness
attributes would be expected to be
selected against in populations.
Nevertheless, such considerations might
be important in certain instances, e.g.,
when evaluating possible effects on
endangered species.
EPA believes it likely that many of the
potential PVCP-PIP/plant combinations
pose a low risk of disrupting the
existing network of ecological
relationships in semi-managed or
natural ecosystems. Multiple conditions
must be met to pose a higher level of
risk, i.e., hybridization with a wild
relative must occur, introgression of the
gene must occur, and acquired virus
resistance must confer an advantage (or
disadvantage) to the recipient plant
sufficient to alter plant population
dynamics. Nevertheless, the research
discussed above showing that in some
cases viruses can affect plant population
dynamics for at least some plants
highlights the difficulty in drawing a
general conclusion as to whether all
PVCP-PIP/plant combinations are likely
to pose a low risk of significantly
disrupting existing ecological networks.
Virtually any crop could be modified to
contain a PVCP-PIP, including less
domesticated forage crops and trees, and
such a wide range of plants will be
associated with a concomitantly wide
range of characteristics and behaviors.
Ecosystems are highly complex and
variable, and some of the factors that
limit fitness of a given plant species can
be subtle and are not well understood
(Ref. 15). Consequently, EPA does not
believe that the available body of
evidence would currently support a
definitive conclusion for all PVCP-PIPs
that the potential transfer to wild or
weedy relatives presents a low risk of
significantly altering the network of
ecological relationships in semimanaged or natural ecosystems.
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Information may be available to
evaluate the likelihood of acquired virus
resistance impacting a particular plant
species or population. However, the
existing body of literature currently
does not appear sufficient to describe
any set of circumstances that would
predict for the wide variety of possible
PVCP-PIP/plant combinations whether
introgression of the PVCP-PIP into a
wild or weedy relative could change the
population dynamics of the recipient
plant and through this route potentially
affect ecological relationships with
other plants and other organisms in the
community. For example, it is not
possible to predict a priori whether a
possible fitness advantage that
individual plants might acquire with a
PVCP-PIP would make the plant
population better able to compete
against other species. Whether
population dynamics would be affected
and ecological relationships could be
disrupted in a given circumstance is
dependent on multiple, interacting
factors. In some instances, a weight-ofevidence, case-by-case review of
information such as experimental data
might allow such a determination;
however, general knowledge of factors
likely to influence population dynamics
cannot be readily distilled into a
straightforward criterion suitable for a
categorical exemption.
2. Proposed exemption criterion. EPA
is proposing § 174.27(a) based on a set
of considerations articulated by the
2005 SAP to identify plants that would
not pose concerns associated with
increased weediness of either the crop
plant itself or any sexually-compatible
wild relatives, if the crop plant were to
contain a PVCP-PIP. Section
174.27(a)(1) is a categorical exemption
criterion for a subset of PVCP-PIPs, i.e.,
a list of plants that have already been
determined by the Agency to be low risk
with respect to concerns associated with
weediness irrespective of the particular
PVCP-PIP the plants might contain.
Section 174.27(a)(2) is a conditional
exemption criterion based on Agency
review of whether a particular plant/
PVCP-PIP combination poses low risk
with respect to concerns associated with
weediness. Both parts of § 174.27(a) are
discussed in more detail in Units
III.E.1.iii. and III.E.1.iv. below. Note that
a PVCP-PIP qualifies for exemption
based in part on its presence in a
particular crop species. The record on
which this proposed exemption is based
is not currently broad enough to support
an exemption for a PVCP-PIP in another
species if that species has not been
evaluated for concerns associated with
weediness when it contains a particular
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virus-resistant trait. A PVCP-PIP that
has been moved into another species
does not qualify for the exemption
unless the recipient plant appears on
the list in § 174.27(a)(1). Such a PVCPPIP would either need an individual
exemption determination under
§ 174.27(a)(2) or a registration in order
to be sold or distributed.
i. Proposed categorical exemption
criterion in § 174.27(a)(1). As articulated
above, EPA does not believe it can
propose a categorical exemption based
on whether a PVCP-PIP/plant
combination is likely to result in
changes in plant population dynamics
because this endpoint cannot easily be
predicted based on straightforward
characteristics of the PVCP-PIP and/or
plant. However, EPA believes that a
criterion for a categorical exemption
could be developed based on evaluation
of individual crop species for their
potential to naturalize and invade
natural ecosystems, including with
acquisition of a PVCP-PIP and for the
existence of wild or weedy relatives that
could acquire a PVCP-PIP through gene
flow. Certain plants are expected to pose
low risk with respect to concerns
associated with weediness regardless of
any particular PVCP-PIP that the species
contained. However, for the categorical
exemption, the Agency is attempting to
identify those situations where no caseby-case review is necessary to conclude
that a PVCP-PIP would present a low
risk of causing adverse effects. In such
situations, a product developer could
use a clearly defined criterion to make
a determination of status. Based on
these considerations, EPA has
developed a list of plants that the
Agency proposes a developer could use
to self-determine whether § 174.27(a) is
met.
A PVCP-PIP would meet proposed
§ 174.27(a) under § 174.27(a)(1) if the
plant containing the PIP is one of the
following: Anthurium (Anthurium spp.),
asparagus (Asparagus officinale),
avocado (Persea americana), banana
(Musa acuminata), barley (Hordeum
vulgare), bean (Phaseolus vulgaris),
cacao (Theobroma cacao), carnation
(Dianthus caryophyllus), chickpea
(Cicer arietinum), citrus (Citrus spp.,
e.g., Citrus aurantifolia, Citrus limon,
Citrus paradisii, Citrus sinensis), coffee
(Coffea arabica and Coffea canephora),
corn (Zea maize), cowpea (Vigna
unguiculata), cucumber (Cucumis
sativus), gerbera (Gerbera spp.),
gladiolus (Gladiolus spp.), lentil (Lens
culinaris), mango (Mangifera indica),
orchids (Orchidaceae), papaya (Carica
papaya), pea (Pisum sativum), peanut
(Arachis hypogaea), pineapple (Ananas
comosus), potato (Solanum tuberosum),
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soybean (Glycine max), starfruit
(Averrhoa carambola), sugarcane
(Saccharum officinarum), or tulips
(Tulipa spp.).
EPA developed this list of plants after
consultations with both the 2004 and
2005 SAPs. The 2004 SAP
recommended a longer list of plants,
chosen initially based on the
presumption that they had no wild or
weedy relatives in the United States.
However, the 2005 SAP noted that the
longer list of plants recommended by
the 2004 SAP clearly contained ‘‘some
species that form viable crop-wild
hybrids...’’ (Ref. 11). Recognizing that
much of the most useful information is
not likely to be found in the literature,
‘‘the Panel recommended consulting
agronomists, breeders, and/or ecologists
with specialized expertise before
including any crop on a list of exempt
species’’ (Ref. 11). The 2005 Panel also
recommended a specific set of
conditions that each species would have
to meet based on the advice of such
experts (i.e., agronomists, breeders, and/
or ecologists with specialized expertise)
if it were to be placed on the list:
1. A crop should be included on the
exempt list if it forms no viable hybrids with
wild or weedy relatives anywhere in the US...
2. A crop should...be included on the
exempt list only if it is [not] currently weedy
or invasive...
3. A crop should be included on the
exempt list if... it will not establish weedy or
invasive populations if it becomes virus
resistant (due to a PVCP-PIP)...
4. If a PVCP-PIP crop has the potential to
naturalize, but the PVCP-PIP transgene is in
biocontainment and/or biomitigation
constructs that are stacked such that escapes
from cultivation are too unfit to compete
with the wild type, a consensus of breeders,
agronomists, and ecologists, or others with
experience with the species could advise
addition to the list (Ref. 11).
EPA believes that the first three
conditions proposed by the 2005 SAP
are useful factors in evaluating whether
a plant warrants inclusion on the list in
§ 174.27(a)(1). EPA considered each of
these factors when evaluating each of
the plants currently on the list in
proposed § 174.27(a)(1). However, EPA
also recognizes that plants that do not
strictly meet condition 1 as laid out by
the SAP may nevertheless be
determined to pose low risk with
respect to weediness concerns after a
case-by-case review of the plants’ traits
and consideration of the whole range of
factors that affect weediness. For
example, corn may not meet the first
condition above as articulated by the
SAP if it proves to in fact have wild
relatives in some region of the United
States with which it can form viable
hybrids. However, as discussed below,
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EPA does not believe that the
characteristics of the wild relatives or
the hybrids that could be formed suggest
any reason to suspect acquired virus
resistance would change the weediness
potential of corn, the hybrid, or the wild
relative, and EPA therefore proposes to
include corn on the list. Thus, in
practice EPA considers the 2005 SAP’s
first three conditions as a useful guide
of the factors that should be taken into
account in evaluating whether to
include a plant on the list. However,
EPA believes that relying on a strict
interpretation of these conditions would
exclude many plants containing PVCPPIPs that meet FIFRA’s low risk
standard. The 2005 SAP itself suggested
that some flexibility of interpretation
might be appropriate. Although the
Panel used the phrase ‘‘no viable
hybrids’’ in condition 1, the Panel
elsewhere recommended against
granting exemption to crops with
‘‘sexually compatible wild relatives’’
where ‘‘sexually compatible refers to the
possibility of having crop transgenes
backcross and introgress into the
relative; it does not refer to sterile
hybrids’’ (Ref. 11).
Although EPA considered the first
three conditions proposed by the 2005
SAP in deciding whether to include a
particular plant species on the list in
§ 174.27(a)(1), EPA believes that the
fourth condition as articulated would be
inappropriate for these purposes. A
biocontainment and/or biomitigation
construct would be associated with a
particular PVCP-PIP, not a particular
plant species. The intent of
§ 174.27(a)(1) is to list species that
would not present concerns related to
weediness regardless of the particular
PVCP-PIP that the species contained.
EPA believes that construct-specific
considerations could be taken into
account under an Agency review
procedure such as that described below
in Unit III.C.2.iii.
The Panel recommended ‘‘consulting
agronomists, breeders, and/or ecologists
with specialized (taxon-specific)
expertise on weedy populations before
including any crop on a list of exempt
species’’ because this information ‘‘is
difficult to ascertain from the literature
and determining the probability that a
crop will be more weedy or invasive if
it contains a PVCP-PIP is even more
difficult.’’ Likewise, the Panel indicated
‘‘[i]t is very difficult to identify crops
that have no sexually compatible wild
or weedy relatives in the US or its
possessions and that do not become
weedy or invasive themselves. This
information is unique to each crop, is
often not published, and is often known
only by the agronomists, breeders, and
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ecologists working with the specific taxa
in question’’ (Ref. 11). EPA agrees that
such information is difficult to obtain
from the literature and therefore relied
on written consultation with such
experts in evaluating whether the three
conditions proposed by the 2005 SAP
had been met for a particular crop
species.
In consulting with experts for a
particular crop, EPA asked at least three
individuals a series of questions
designed to address the issues identified
by the 2005 SAP as relevant for
evaluating whether a PVCP-PIP would
be low risk with respect to concerns
associated with weediness if it were to
be found in the particular species.
Specifically, EPA wanted to know:
• Does this crop form viable hybrids in
nature (i.e., without human
intervention) with wild or weedy
relatives in the United States (including
Puerto Rico, the Virgin Islands, Guam,
the Trust Territory of the Pacific Islands,
and American Samoa)?
If yes, what species are they? Which
of these species are themselves
commercially grown crops? What is the
frequency of hybrid production? Have
hybrids demonstrated enhanced fitness
(vigor) relative to parental varieties? Can
the hybrids reproduce asexually? Are
the hybrids sexually fertile?
If hybrids are sexually fertile, will
they outcross or only backcross with the
crop parent? How does the phenology of
the crop species compare with the
phenology of plant(s) with which it is
sexually compatible? Are there any
other attributes of these species that
may enhance or inhibit sexual
reproduction and species out-crossing?
• Is this crop known to become feral
or easily spread into non-crop areas in
the United States (including Puerto
Rico, the Virgin Islands, Guam, the
Trust Territory of the Pacific Islands,
and American Samoa)? If yes, have
escaped plants formed reproducing and
sustaining populations in non-crop
areas? Where has this been known to
happen? With what frequency is this
likely to occur? Have feral populations
required weed management activity?
• How likely is it that this crop would
become feral or easily spread into noncrop areas if it acquired transgenic
resistance to one or more viruses? What
is the basis for your answer?
EPA focused these questions on ‘‘noncrop areas’’ to emphasize that the key
consideration is a crop’s behavior in
natural settings. EPA recognizes that
most crops within agricultural fields
form volunteer populations, where
propagules of the crop from the
previous rotation grow in the
subsequent crop rotation. The Agency
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did not consider behavior in crop areas
when evaluating the crops for inclusion
on the list at proposed § 174.27(a)(1).
The responses to specific Agencyposed questions received from these
expert consultations are available in the
docket for this proposed rule (Ref. 42).
EPA considered the experts’ responses
in conjunction with other information
when determining whether to list a crop
at proposed § 174.27(a)(1), as discussed
below. Crops that EPA evaluated but did
not include in the proposed list for one
reason or another are discussed in Unit
VII where comment on these crops is
specifically requested.
EPA notes that the 2005 SAP also
suggested the Agency ‘‘consider the
geographic distribution of crops and
their wild relatives when considering
potential exemptions’’ (Ref. 11).
Although this is a potential option the
Agency could pursue, a number of
considerations limit the utility of using
the potential for geographic isolation in
determining whether a plant could be
included on the list in § 174.27(a)(1).
For example, EPA would need to
consider carefully whether such
isolation is likely to remain throughout
the commercial life of the PVCP-PIP.
Such isolation could occur if the crop
containing the PVCP-PIP would not be
commercially viable in the areas where
wild relatives occur given biological
considerations that are unlikely to
change. However, geographic isolation
could also be due to factors that may
change throughout the commercial life
of a PVCP-PIP, e.g., individual farmer
choices of which crops to plant. Because
of such considerations, EPA anticipates
that it would only be able to support an
exemption dependant on geographic
restrictions where biological or similar
factors provide assurance that the
geographic isolation will remain
constant during the entire commercial
life of the PVCP-PIP.
The next several Subunits summarize
EPA’s conclusions to include the crops
listed at proposed § 174.27(a)(1) based
on consideration of the conditions
suggested by the 2005 SAP and their
recommendation that evaluation of
these conditions be done in consultation
with breeders, agronomists, and
ecologists familiar with the particular
species. The analyses below indicate
that there is an extremely low
probability that virus resistance
conferred through a PVCP-PIP in any of
these plants would significantly alter
existing plant population dynamics or
existing ecological relationships. The
list is straightforward, providing an
easy-to-understand criterion.
Accordingly, EPA is proposing that a
developer may self-determine whether a
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PVCP-PIP meets this criterion, i.e.,
whether the plant containing the PVCPPIP is on the proposed list, because no
further data or information would be
needed to evaluate whether ecological
relationships could be disrupted
through increased weediness when the
plant modified to contain the PVCP-PIP
is on the list.
a. Anthurium. EPA proposes that
anthurium (Anthurium spp.) be
included on the list in § 174.27(a)(1)
based on EPA consultations with
anthurium experts. These consultations
indicate that anthurium meets the three
conditions outlined above by the SAP:
It does not have wild or weedy relatives
in the United States with which it can
form viable hybrids in nature, it is not
currently weedy or invasive in the
United States, and there is no reason to
believe that acquisition of virus
resistance would make anthurium
weedy or invasive. All three experts
contacted by EPA indicated agreement
with these statements. For example, one
expert stated, ‘‘The commercial species
[of] Anthurium (Anthurium
schezerianum and Anthurium
andraenum) have been grown outdoors
since the early 1900’s in semi-tropical
and tropical areas of the US and there
are no records of any commercial
species escaping and becoming feral
into non-crop areas. There is no reason
to believe that acquiring transgenic
resistance to one or more viruses would
increase the ability of plants to become
feral or easily spread into non-crop
areas’’ (Ref. 42). EPA therefore believes
that anthurium meets the conditions
recommended by the 2005 SAP for
inclusion on the list and will present
low risk with respect to weediness.
b. Asparagus. EPA proposes that
asparagus (Asparagus officinale) be
included on the list in § 174.27(a)(1)
based on EPA consultations with
asparagus experts. These consultations
indicate that asparagus meets the three
conditions outlined above by the SAP.
One, it does not have wild or weedy
relatives in the United States with
which it can form viable hybrids in
nature. One expert said, ‘‘Although
volunteer asparagus plants may grow
‘‘wild’’ (i.e., not intentionally
cultivated), they are not typically
considered to be weeds. There are
several horticultural varieties of
asparagus, which could potentially be
cross-pollinated. However, considering
that asparagus is insect pollinated, this
is likely to occur only in the rare
situation where an asparagus grower
also is growing horticultural varieties’’
(Ref. 42). Second, the experts agreed
that asparagus is not currently weedy or
invasive outside of agricultural fields in
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the United States. Two of the three
experts indicated that asparagus can
infrequently become feral. However,
‘‘[a]sparagus is not typically considered
to be a weedy species. In addition, since
asparagus has separate male and female
plants, it is considerably more difficult
for ‘‘wild’’ populations to become
established. Asparagus is also a
relatively slow growing plant such that
eradication (if necessary) would not be
particularly onerous’’ (Ref. 42). Third,
these experts agreed that it is unlikely
that acquisition of virus resistance
would make asparagus weedy or
invasive. For example, one expert
stated, ‘‘I have worked with this crop
since 1978 and in all those years, I have
not observed asparagus to become easily
spread at all in non-crop or crop areas.
Although asparagus does rarely grow
wild in some areas (usually the
temperate zones) asparagus is a very
poor competitor with weeds and other
plants and asparagus requires much
attention and cultural care to thrive. I
have only viewed a very rare
occassionaly [sic] plant along fence
rows and they usually are very weak
and non-vigorous. Acquired transgenic
resistance would do nothing to affect
asparagus to become feral’’ (Ref. 42).
EPA therefore believes that asparagus
meets the conditions recommended by
the 2005 SAP for inclusion on the list
and will present low risk with respect
to weediness.
c. Avocado. EPA proposes that
avocado (Persea americana) be included
on the list in § 174.27(a)(1) based on
EPA consultations with avocado
experts. These consultations indicate
that avocado meets the three conditions
outlined above by the SAP: It does not
have wild or weedy relatives in the
United States with which it can form
viable hybrids in nature, it is not
currently weedy or invasive in the
United States, and there is no reason to
believe that acquisition of virus
resistance would make avocado weedy
or invasive. All three experts contacted
by EPA indicated agreement with these
statements. For example, one expert
stated ‘‘Transgenic resistance should not
affect the likelihood of spread. Viral
susceptibility is not an important factor
limiting the plant’s ability to become
feral’’ (Ref. 42). EPA therefore believes
that avocado meets the conditions
recommended by the 2005 SAP for
inclusion on the list and will present
low risk with respect to weediness.
d. Banana. EPA proposes that banana
(Musa acuminata) be included on the
list in § 174.27(a)(1) based on EPA
consultations with banana experts.
These consultations indicate that
banana meets the three conditions
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outlined above by the SAP: It does not
have wild or weedy relatives in the
United States with which it can form
viable hybrids in nature, it is not
currently weedy or invasive in the
United States, and there is no reason to
believe that acquisition of virus
resistance would make banana weedy or
invasive. All three experts contacted by
EPA indicated agreement with these
statements. For example, one expert
stated ‘‘[i]t is highly unlikely that
banana with acquired transgenic
resistance would spread to non-crop
areas because the probability of crossing
is extremely small. Through vegetative
propagation it will require man [sic]
intervention just as non-transgenic
plants’’ (Ref. 42). EPA therefore believes
that banana meets the conditions
recommended by the 2005 SAP for
inclusion on the list and will present
low risk with respect to weediness.
e. Barley. EPA proposes that barley
(Hordeum vulgare) be included on the
list in § 174.27(a)(1) based on EPA
consultations with barley experts. These
consultations indicate that barley meets
the three conditions outlined above by
the SAP: It does not have wild or weedy
relatives in the United States with
which it can form viable hybrids in
nature, it is not currently weedy or
invasive in the United States, and there
is no reason to believe that acquisition
of virus resistance would make barley
weedy or invasive, as viruses are not
consistently associated with failure of
barley to show any evidence of being
weedy or invasive. Three experts
contacted by EPA indicated agreement
with these statements. For example, one
expert stated that he believes the
likelihood that barley would become
feral or easily spread into non-crop
areas if it acquired transgenic virus
resistance is ‘‘negligible. Barley has
been cultivated for decades in many
U.S. environments, including
environments that impose relatively
mild disease pressure, particularly for
viral diseases, such as the upper
midwest and western states, and barley
has not been able to establish itself in
those regions as a feral species’’ (Ref.
42). EPA notes that the 2005 SAP
indicated that ‘‘barley can hybridize
with Hordeum jubatum, which is a
weed in the USA’’ (Ref. 11). However,
three barley breeders consulted about
this specific issue did not agree that
hybridization was likely to occur. One
stated, ‘‘In relation to Hordeum vulgare
subsp. Vulgare (cultivated barley)
Hordeum jubatum is in the tertiary
genepool. This means crossability is
extremely difficult event under
laboratory conditions’’ (Ref. 42). A study
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that attempted to cross barley with two
wild relatives, H. murinum L. and H.
jubatum L., found that no hybridization
occurred, even under favorable
greenhouse conditions with forced
pollination (Ref. 43). EPA therefore
believes that barley meets the
conditions recommended by the 2005
SAP for inclusion on the list and will
present low risk with respect to
weediness.
f. Bean. EPA proposes that bean
(Phaseolus vulgaris) be included on the
list in § 174.27(a)(1) based on EPA
consultations with bean experts. These
consultations indicate that bean meets
the three conditions outlined above by
the SAP. One, it does not have wild or
weedy relatives in the United States
with which it can form viable hybrids
in nature. One expert mentioned that
‘‘[h]ybrids between Phaseolus vulgaris
and Phaseolus acutifolius (tepary bean)
are only achieved through extensive
crossing and embryo rescue and thus is
highly unlikely to occur in nature’’ (Ref.
42). Another expert said bean would
‘‘only - but rarely - hybridize with wild
vulgaris (only where wild vulgaris
occur, generally not in [the United
States] & there are often biological
barriers to such occurring’’ (Ref. 42).
Second, these experts agreed that bean
is not currently weedy or invasive in the
United States. Third, these experts
agreed that it is unlikely that acquisition
of virus resistance would make bean
weedy or invasive. For example, one
expert stated, ‘‘Viruses generally do not
prevent susceptible beans from making
a crop (just the yield and quality of the
crop is greatly reduced’’ (Ref. 42). EPA
therefore believes that bean meets the
conditions recommended by the 2005
SAP for inclusion on the list and will
present low risk with respect to
weediness.
g. Cacao. EPA proposes that cacao
(Theobroma cacao) be included on the
list in § 174.27(a)(1) based on EPA
consultations with cacao experts. These
consultations indicate that cacao meets
the three conditions outlined above by
the SAP: It does not have wild or weedy
relatives in the United States with
which it can form viable hybrids in
nature, it is not currently weedy or
invasive in the United States, and there
is no reason to believe that acquisition
of virus resistance would make cacao
weedy or invasive. All three experts
contacted by EPA indicated agreement
with these statements. For example, one
expert stated that ‘‘cacao is difficult to
cultivate, the seeds are very susceptible
to desiccation, and germination must
occur within a few days or the seed die
[sic]’’ (Ref. 42). EPA therefore believes
that cacao meets the conditions
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recommended by the 2005 SAP for
inclusion on the list and will present
low risk with respect to weediness.
h. Carnation. EPA proposes that
carnation (Dianthus caryophyllus) be
included on the list in § 174.27(a)(1)
based on EPA consultations with
carnation experts. These consultations
indicate that carnation meets the three
conditions outlined above by the SAP.
One, it does not have wild or weedy
relatives in the United States with
which it can form viable hybrids in
nature. Two, it is not currently weedy
or invasive in the United States. One
expert indicated that Arkansas and
Massachusetts have populations of feral
Dianthus caryophyllus. However these
have not required management activity
because ‘‘populations have remained
small consisting of only a few plants’’
(Ref. 42). Three, there is no reason to
believe that acquisition of virus
resistance would make carnation weedy
or invasive. One expert stated, ‘‘Most
species of Dianthus are selfincompatible, and commercial
selections of carnation require hand
pollination, and set little viable seed.
There is no record of carnation, D.
caryophyllus, being naturalized or
invasive in any part of the world’’ (Ref.
42). EPA therefore believes that
carnation meets the conditions
recommended by the 2005 SAP for
inclusion on the list and will present
low risk with respect to weediness.
i. Chickpea. EPA proposes that
chickpea (Cicer arietinum) be included
on the list in § 174.27(a)(1) based on
EPA consultations with chickpea
experts. These consultations indicate
that chickpea meets the three conditions
outlined above by the SAP: It does not
have wild or weedy relatives in the
United States with which it can form
viable hybrids in nature, it is not
currently weedy or invasive in the
United States, and there is no reason to
believe that acquisition of virus
resistance would make chickpea weedy
or invasive. All three experts contacted
by EPA indicated agreement with these
statements. For example, one expert
stated that ‘‘there is no chance that
chickpea would become feral with or
without virus resistance. The
susceptibility of the seeds to rotting
without seed treatment would prevent
any spread to non-crop areas. Resistance
to viruses would not affect this
outcome’’ (Ref. 42). EPA therefore
believes that chickpea meets the
conditions recommended by the 2005
SAP for inclusion on the list and will
present low risk with respect to
weediness.
j. Citrus. EPA proposes that citrus
(Citrus spp.) be included on the list in
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§ 174.27(a)(1) based on EPA
consultations with citrus experts. These
consultations indicate that citrus meets
the three conditions outlined above by
the SAP. One, it does not have wild or
weedy relatives in the United States
with which it can form viable hybrids
in nature. One expert mentioned that
citrus can hybridize with other Citrus
species and certain other closely related
species in the sub-family Aurantioidea.
However, this expert also noted that it
was unlikely to hybridize naturally with
any of these species that are found in
the United States because they are not
closely related and ‘‘would only be in
the tertiary genepool for citrus’’ (Ref.
42). Another expert pointed out that
Rangpur lime is sometimes mentioned
as native to Florida, but he did not think
this was true; as far as he knew, there
are no wild or weedy relatives of citrus
found in the United States. Second,
these experts agreed that citrus is not
currently weedy or invasive in the
United States. One expert mentioned
that there are ‘‘small feral populations of
citrus found in Florida, mostly on the
borders of the Everglades area and in
some old forests.... However, these
populations have not expanded their
range. I know of no weed management
efforts’’ (Ref. 42). Third, these experts
agreed that it is unlikely that acquisition
of virus resistance would make citrus
weedy or invasive. For example, one
expert stated that ‘‘citrus is simply not
an aggressive grower with or without a
virus’’ (Ref. 42). EPA therefore believes
that Citrus species meet the conditions
recommended by the 2005 SAP for
inclusion on the list and will present
low risk with respect to weediness.
k. Coffee. EPA proposes that coffee
(Coffea arabica and Coffea canephora)
be included on the list in § 174.27(a)(1)
based on EPA consultations with coffee
experts. These consultations indicate
that both species of coffee meet the
three conditions outlined above by the
SAP: They do not have wild or weedy
relatives in the United States with
which they can form viable hybrids in
nature, they are not currently weedy or
invasive in the United States, and there
is no reason to believe that acquisition
of virus resistance would make coffee
weedy or invasive. All three experts
contacted by EPA indicated agreement
with these statements. For example, one
expert stated, ‘‘Coffee plantations that
are abandoned usually decay and are
not overtaken by coffee plants. The crop
needs maintenance to grow properly. It
is not a weedy species’’ (Ref. 42). EPA
therefore believes that coffee meets the
conditions recommended by the 2005
SAP for inclusion on the list and will
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present low risk with respect to
weediness.
l. Corn. EPA proposes that corn
(maize; Zea mays) be included on the
list in § 174.27(a)(1) based on EPA’s
extensive experience regulating PIPs in
corn (Ref. 44), literature that is available
on corn biology, the OECD Consensus
Document on the Biology of Zea mays
subsp. mays (Maize) (Ref. 45), and EPA
consultations with corn experts (Ref.
42). OECD consensus documents are
written by national experts who freely
consult with breeders, agronomists, and
ecologists who are specialists in the
field. Each document must be reviewed
and approved by experts in the 30
OECD member countries, and often by
experts from non-OECD member
countries. This body of information
indicates that corn is low risk with
respect to concerns associated with
weediness.
EPA’s 2001 risk assessment for Bt PIPs
evaluated the potential for corn to form
viable hybrids with wild or weedy
relatives in the United States (Ref. 44).
EPA’s summary conclusion was that
while wild relatives of corn (i.e., Eastern
Gama Grass and teosintes) may exist in
the United States, there is no significant
risk of gene capture and expression of
a PIP in any of these relatives. The
potential for pollen-directed gene flow
from corn to Eastern Gama Grass is
extremely remote. This is evidenced by
the difficulty with which Tripsacum
dactyloides x Zea mays hybrids are
produced in structured breeding
programs. Additionally, the genus does
not represent any species considered as
serious or pernicious weeds in the
United States or its territories. Any
introgression of genes into this species
as a result of cross fertilization with
genetically modified corn is not
expected to result in a species that is
weedy or difficult to control. In many
instances where hybridization has been
directed between these two species, the
resultant genome is lacking in most or
all of the corn chromosomal
complement in subsequent generations.
Many of the Zea species loosely referred
to as ‘‘teosintes’’ will produce viable
offspring when crossed with Zea mays
ssp. mays. None of these plants are
known to harbor weedy characteristics,
and none of the native teosinte species,
subspecies, or races are considered to be
aggressive weeds in their native or
introduced habitats. In fact, many are on
the brink of extinction where they are
indigenous and will be lost without
human intervention (i.e., conservation
measures). Two of the three experts EPA
consulted indicated that corn will not
form viable hybrids with any wild or
weedy relatives in the United States.
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The third indicated that hybrids could
be formed with teosintes, but that a
hybrid ‘‘would lose its seed dispersal
ability, so would have highly
diminished ability to propagate in the
wild. In regions where teosinte is a
weed (mostly in Mexico), the teosintes
have been naturally selected to have
‘gametophyte factors’ (e.g., Ga1-s, Tcb1),
that essentially block corn pollen from
fertilizing teosinte’’ (Ref. 42).
Further, the body of information and
the experts that EPA consulted on corn
indicate that it is not currently weedy or
invasive in the United States. None of
the landraces or cultivated lines of Zea
mays are considered to have weedy
potential, and all are generally
considered to be incapable of survival in
the wild as a result of breeding practices
(i.e., selection) during domestication of
the crop. According to the OECD
consensus document, ‘‘[m]aize has lost
the ability to survive in the wild due to
its long process of domestication, and
needs human intervention to
disseminate its seed. Although corn
from the previous crop year can
overwinter and germinate the following
year, it cannot persist as a weed’’ (Ref.
45). One expert EPA consulted stated,
‘‘Maize does not become feral or spread
easily into non-crop areas in the United
States or its territories. During its
domestication many centuries ago,
maize lost many of the attributes
necessary to sustain itself in nature’’
(Ref. 42).
Finally, there is no reason to believe
that acquisition of virus resistance
would make corn weedy or invasive, as
viruses are not consistently associated
with failure of corn to show any
evidence of being weedy or invasive.
The experts EPA consulted agree that
corn’s becoming weedy with acquisition
of a PVCP-PIP is unlikely. For example,
one expert indicated, ‘‘Domesticated
maize has no seed dispersal mechanism.
Humans are required to remove kernels
from the cob (a typical cob holds 500–
1,000 kernels, which would essentially
try to all grow in the same spot, this
would starve the resulting plants for
nutrients and water and result in there
being no progeny). Maize would
essentially die out within a year or two,
without human intervention’’ (Ref. 42).
EPA therefore believes that corn meets
the conditions recommended by the
2005 SAP for inclusion on the
§ 174.27(a)(1) list and will present low
risk with respect to weediness.
m. Cowpea. EPA proposes that
cowpea (black-eyed pea; Vigna
unguiculata) be included on the list in
§ 174.27(a)(1) based on EPA
consultations with cowpea experts.
These consultations indicate that
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cowpea meets the three conditions
outlined above by the SAP. One, it does
not have wild or weedy relatives in the
United States with which it can form
viable hybrids in nature. One expert
indicated, ‘‘the cowpea is a highly selfpollinating crop that rarely outcrosses
with other cowpeas. I expect that it
might be possible for cowpea to rarely
outcross with a ‘wild’ V. unguiculata,
but it is probably safe to assume that the
‘wild’ cowpea genotypes don’t exist in
the United States’’ (Ref. 42). Second, the
experts agreed that cowpea is not
currently weedy or invasive outside of
agricultural fields in the United States.
One expert said, ‘‘I am not aware of any
instance where the cowpea has become
feral or easily spread into non-crop
areas in the United States. HOWEVER,
I am aware of instances where
cultivated cowpea varieties have
become weed pests in cultivated areas
in the United States where OTHER
CROPS are grown. For example, cowpea
varieties with hard seeds can be a weed
problem in soybean crops. The hard
cowpea seeds over-winter in the soil
and can produce plants in subsequent
years; these cowpea plants often can’t be
easily killed by soybean herbicides
(closely related plant) and the seeds are
often so close in size to soybean seeds
that [they] can be difficult to remove
from the harvested soybean product’’
(Ref. 42). However, EPA considers that
the key consideration is the plant’s
behavior in natural settings, including
semi-managed habitat surrounding
agricultural fields, as opposed to its
behavior within the fields themselves.
Third, these experts agreed that it is
unlikely that acquisition of virus
resistance would make cowpea weedy
or invasive. For example, one expert
stated ‘‘I am not aware of any virus
problem in cowpea, if resolved via
transgenic means, would result in the
crop becoming feral’’ (Ref. 42). EPA
therefore believes that cowpea meets the
conditions recommended by the 2005
SAP for inclusion on the list and will
present low risk with respect to
weediness.
n. Cucumber. EPA proposes that
cucumber (Cucumis sativus) be
included on the list in § 174.27(a)(1)
based on EPA consultations with
cucumber experts. These consultations
indicate that cucumber meets the three
conditions outlined above by the SAP:
It does not have wild or weedy relatives
in the United States with which it can
form viable hybrids in nature, it is not
currently weedy or invasive in the
United States, and there is no reason to
believe that acquisition of virus
resistance would make cucumber weedy
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or invasive. The experts contacted by
EPA indicated agreement with these
statements. For example, one expert
stated that ‘‘cucumber could not become
feral due to acquired transgenic virus
resistance. The failure for [cucumber] to
survive without human intervention is
not due to disease attack, but rather due
to [its] ability to compete with native
plants and weeds, and to withstand the
stresses they are exposed to outside of
cultivation, particularly drought’’ (Ref.
42). EPA therefore believes that
cucumber meets the conditions
recommended by the 2005 SAP for
inclusion on the list and will present
low risk with respect to weediness.
o. Gerbera. EPA proposes that gerbera
(Gerbera spp.) be included on the list in
§ 174.27(a)(1) based on EPA
consultations with gerbera experts. Two
experts indicated that there are no wild
or weedy relatives in the United States
with which gerbera can form viable
hybrids in nature. A third said,
‘‘Gerbera jamesonii Bolus ex Adlam has
been recorded as naturalized in Florida.
However, it is most likely Gerbera
hybrida (Gerbera jamesonii x G.
viridiflora Schultz-Bip) which is the
designation for the commercially
available Gerberas’’ (Ref. 42). Regarding
the ferality of gerbera species, two
experts believed feral populations were
not known to occur, while a third noted,
‘‘Although G. jamesonii (or G. hybrida)
is attributed to Florida, it is most likely
a low risk for forming feral populations’’
(Ref. 42). All three experts believed it
unlikely that acquired virus resistance
could lead to gerbera becoming feral or
easily spreading into non-crop areas.
One expert said, ‘‘Gerbera, in general, is
a short-lived perennial in the United
States. It suffers from a number of fungal
and bacteria pathogens. A transgenic
virus-resistant Gerbera offers little in
terms of [increased] fitness and
increased invasive potential’’ (Ref. 42).
p. Gladiolus. EPA proposes that
gladiolus (Gladiolus spp.) be included
on the list in § 174.27(a)(1) based on
EPA consultations with gladiolus
experts. These consultations indicate
that gladiolus meets the three
conditions outlined above by the SAP:
It does not have wild or weedy relatives
in the United States with which it can
form viable hybrids in nature, it is not
currently weedy or invasive in the
United States, and there is no reason to
believe that acquisition of virus
resistance would make gladiolus weedy
or invasive. The experts contacted by
EPA indicated agreement with these
statements. For example, one expert
said, ‘‘No gladiolus species or hybrid
has ever been documented as having
successfully naturalized in the United
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States. Virus resistance is not likely to
make this any more likely’’ (Ref. 42).
EPA therefore believes that gladiolus
meets the conditions recommended by
the 2005 SAP for inclusion on the list
and will present low risk with respect
to weediness.
q. Lentil. EPA proposes that lentil
(Lens culinaris) be included on the list
in § 174.27(a)(1) based on EPA
consultations with lentil experts.
Although lentil was not on the list of
plants recommended by the 2004 SAP,
several experts consulted about other
crops mentioned that lentil also
appeared to meet the criteria that EPA
was investigating. Consultations about
lentil indicate that it meets the three
conditions outlined above by the SAP:
It does not have wild or weedy relatives
in the United States with which it can
form viable hybrids in nature, it is not
currently weedy or invasive in the
United States, and there is no reason to
believe that acquisition of virus
resistance would make lentil weedy or
invasive. The experts contacted by EPA
indicated agreement with these
statements. For example, one expert
stated, ‘‘Lentil could not possibly
survive in the wild on its own. [Lentils
are] rather delicate plants, small in
stature and very weak in competition for
space or water. It needs great care from
grower [sic] to produce seeds in
cultivation. Its seed could not possibly
survive in the wild due to rotting by
soil-born microorganisms. Resistance to
one or more viruses will not increase
the survivability of lentil seeds in the
wild’’ (Ref. 42). EPA therefore believes
that lentil meets the conditions
recommended by the 2005 SAP for
inclusion on the list and will present
low risk with respect to weediness.
r. Mango. EPA proposes that mango
(Mangifera indica) be included on the
list in § 174.27(a)(1) based on EPA
consultations with mango experts.
These consultations indicate that mango
meets the three conditions outlined
above by the SAP: It does not have wild
or weedy relatives in the United States
with which it can form viable hybrids
in nature, it is not currently weedy or
invasive in the United States, and there
is no reason to believe that acquisition
of virus resistance would make mango
weedy or invasive. All three experts
contacted by EPA indicated agreement
with these statements. For example, one
expert stated, ‘‘spread of mango seed by
humans or animals into non-crop areas
is rare and suitable environments are
few. Transgenic resistance should not
affect the likelihood of spread. Viral
susceptibility is not an important factor
limiting the plant’s ability to become
feral’’ (Ref. 42). EPA therefore believes
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that mango meets the conditions
recommended by the 2005 SAP for
inclusion on the list and will present
low risk with respect to weediness.
s. Orchids. EPA proposes that all
genera of orchids in the family
Orchidaceae be included on the list in
§ 174.27(a)(1) based on EPA
consultations with orchid experts.
These consultations indicate that
orchids meet the three conditions
outlined above by the SAP: They do not
have wild or weedy relatives in the
United States with which they can form
viable hybrids in nature, they are not
currently weedy or invasive in the
United States, and there is no reason to
believe that acquisition of virus
resistance would make orchids weedy
or invasive. All three experts contacted
by EPA indicated agreement with these
statements. For example, one expert
stated, ‘‘Species within these genera
have specific insect pollinators and
those insects are unlikely [to] be present
for pollination in United States. In
addition, species within these genera
are very difficult to grow from seed
without human intervention, requiring a
symbiotic relationship with a specific
fungal species. Acquiring transgenic
resistance to one or more viruses would
not affect pollination or seed
germination’’ (Ref. 42). EPA therefore
believes that species in the orchid
family meet the conditions
recommended by the 2005 SAP for
inclusion on the list and will present
low risk with respect to weediness.
t. Papaya. EPA proposes that papaya
(Carica papaya) be included on the list
in § 174.27(a)(1) based on EPA
consultations with papaya experts.
These consultations indicate that
papaya meets the three conditions
outlined above by the SAP. First, it does
not have wild or weedy relatives in the
United States with which it can form
viable hybrids in nature. Although
Carica papaya has been successfully
crossed with Vasconellea species using
laboratory-based embryo rescue
techniques, such hybrids do not form in
nature (Ref. 42). Second, although all
three breeding experts agreed that
papaya is known to establish outside of
agricultural areas through human- and
animal-mediated seed dispersal, the
species is not considered to be weedy or
invasive. For example, one expert
stated, ‘‘I have observed small feral
[papaya] populations in Guam, Hawaii
and Puerto Rico... in areas close to
human dwellings and activities.... The
feral papayas are not weedy and are
nonaggressive, they can easily be
removed by cutting down.’’ Further, as
stated in USDA-APHIS’ response to a
petition for determination of
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nonregulated status for transgenic virusresistant papaya, ‘‘Papaya is not listed
as a weed in the Federal Noxious Weed
Act (7 U.S.C. 2801–2813) and is not
reported by the Weed Society of
America to be a common or troublesome
weed anywhere in the United States
(Bridges and Bauman, 1992; Holm et al.
1979; Muenscher, 1980)’’ (Ref. 46).
Third, two of three experts indicate
there is no reason to believe that
acquisition of virus resistance would
make papaya weedy or invasive. The
third expert said that it was ‘‘[v]ery
likely’’ papaya would become feral or
easily spread into non-crop areas if it
acquired transgenic resistance to one or
more viruses because ‘‘[a]necdotal and
informal reports at papaya conferences
gave evidence that the virus resistance
transgene was found in feral
populations’’ (Ref. 42). However, this
comment seems to reflect the fact, as
noted above, that papaya does
occasionally form feral populations in
spite of not being weedy or aggressive,
and this characteristic would be
expected whether the papaya is
transgenic or not. In his comments to
EPA, another expert concludes by
saying that territorial records show
papaya was not a weed in Hawaii prior
to the discovery of papaya viruses in the
1940s. If papaya was not considered a
weed prior to exposure to viruses, then
there is no reason to believe that a virus
resistant papaya would become a weed.
Another expert corroborates this
conclusion by stating, ‘‘I see no
competitive advantage of [virusresistant] transgenic papayas over
nontransgenic papayas.... Papaya
requires high levels of human inputs to
thrive or survive, including fertilizers,
chemicals and care’’ (Ref. 42). EPA
therefore believes that papaya meets the
conditions recommended by the 2005
SAP for inclusion on the list and will
present low risk with respect to
weediness.
u. Pea. EPA proposes that pea (Pisum
sativum) be included on the list in
§ 174.27(a)(1) based on EPA
consultations with pea experts. These
consultations indicate that pea meets
the three conditions outlined above by
the SAP: It does not have wild or weedy
relatives in the United States with
which it can form viable hybrids in
nature, it is not currently weedy or
invasive in the United States, and there
is no reason to believe that acquisition
of virus resistance would make pea
weedy or invasive. All three experts
contacted by EPA indicated agreement
with these statements. For example, one
expert stated, ‘‘pea is not likely to
become feral or easily spread into non-
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crop areas due to acquired resistance to
one or more viruses. Acquisition of
transgenic viral resistance would not
provide any adaptive advantage for
survival of the transgenic crop plants.
Peas have been produced in the US for
more than 75 years with infrequent viral
epidemics (5–9 year cycles) and no feral
populations of pea have been recorded;
therefore environmental and cultural
conditions are the more likely agent
preventing establishment of feral
populations’’ (Ref. 42). EPA therefore
believes that pea meets the conditions
recommended by the 2005 SAP for
inclusion on the list and will present
low risk with respect to weediness.
v. Peanut. EPA proposes that peanut
(Arachis hypogaea) be included on the
list in § 174.27(a)(1) based on EPA
consultations with peanut experts.
These consultations indicate that peanut
meets the three conditions outlined
above by the SAP: It does not have wild
or weedy relatives in the United States
with which it can form viable hybrids
in nature, it is not currently weedy or
invasive in the United States, and there
is no reason to believe that acquisition
of virus resistance would make peanut
weedy or invasive. All three experts
contacted by EPA indicated agreement
with these statements. For example, one
expert stated, ‘‘virus pressure is not the
limiting factor. Even without virus
pressure peanut (Arachis hypogaea) are
not able to become feral or easily spread
into non-crop areas. Peanut are not able
to sustain long term natural populations
without cultivation by man’’ (Ref. 42).
EPA therefore believes that peanut
meets the conditions recommended by
the 2005 SAP for inclusion on the list
and will present low risk with respect
to weediness.
w. Pineapple. EPA proposes that
pineapple (Ananas comosus) be
included on the list in § 174.27(a)(1)
based on EPA consultations with
pineapple experts. These consultations
indicate that pineapple meets the three
conditions outlined above by the SAP.
One, it does not have wild or weedy
relatives in the United States with
which it can form viable hybrids in
nature. One expert indicated, ‘‘The
taxonomy of the genus Ananas was
recently critically reviewed and revised
(Chan et al., 2003) and all of the wild
relatives of pineapple are classified in
the same genus and species as the
cultivated pineapple but are different
botanical varieties. These are Ananas
comosus var. ananassoides and A.
comosus var. parguazensis (Chan et al.,
2003). If these wild relatives are found
in the United States and its territories
they would be in cultivated gardens or
in pots. There are no reports that A.
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comosus var comosus or its wild
relatives survive naturally in the wild or
pose a potential threat as weed species.
If natural crosses between Ananas
species occur in nature, it is highly
unlikely that seed produced from them
would survive to produce a mature
plant’’ (Refs. 42 and 47). Second, the
experts agreed that pineapple is not
currently weedy or invasive in the
United States. Third, these experts
agreed that it is unlikely that acquisition
of virus resistance would make
pineapple weedy or invasive. For
example, one expert stated, ‘‘Assuming
transgenic plants were resistant to all
known pests, pineapple still cannot
compete with weeds, which quickly
overtop slower growing pineapple
plants. Pineapple lacks any natural
mechanism for vegetative propagation
and does not propagate naturally by
seeds because seedlings are delicate and
require special care to survive to
maturity’’ (Ref. 42). EPA therefore
believes that pineapple meets the
conditions recommended by the 2005
SAP for inclusion on the list and will
present low risk with respect to
weediness.
x. Potato. EPA proposes that potato
(Solanum tuberosum) be included on
the list in § 174.27(a)(1) based on the
Agency’s experience regulating PIPs in
potato (Ref. 44), literature that is
available on potato biology, the OECD
Consensus Document on the Biology of
Solanum tuberosum subsp. tuberosum
(Potato) (Ref. 48), and EPA consultations
with potato experts (Ref. 42). This body
of information indicates that potato is
low risk with respect to concerns
associated with weediness.
EPA’s 2001 risk assessment for Bt
PIPs evaluated the potential for potato
to form viable hybrids with wild or
weedy relatives in the United States
(Ref. 44). EPA’s conclusion was that
there is no foreseeable risk of gene
capture and PIP expression in wild
relatives of Solanum tuberosum in the
United States. Successful gene
introgression into tuber-bearing
Solanum species is virtually excluded
due to constraints of geographical
isolation and other biological barriers to
natural hybridization (Ref. 49). These
barriers include incompatible (unequal)
endosperm balance numbers that lead to
endosperm failure and embryo abortion,
multiple ploidy levels, and
incompatibility mechanisms that do not
express reciprocal genes to allow
fertilization to proceed. No natural
hybrids have been observed between
these species and cultivated potatoes in
the United States.
The body of information EPA
consulted on potato also indicates that
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the crop is not currently weedy or
invasive in the United States. According
to the OECD consensus document,
‘‘[o]utside the field, potato seedlings
will have difficulty establishing
themselves as they cannot compete with
other plants. Love et al., 1994 report that
these seedlings are limited to cultivated
areas for reasons of competition and
adaptation. Potato tubers can be spread
during transportation and use, but
generally these plants will not be
established for a long time due to
unfavourable environmental conditions.
In general, the potato is not known as
a coloniser of unmanaged ecosystems’’
(Ref. 48). One expert EPA consulted
indicated potato ‘‘is a rare weed in
potato plots but it never becomes feral
in the United States’’ (Ref. 42).
Finally, there is no reason to believe
that acquisition of virus resistance
would make potato weedy or invasive,
as viruses are not consistently
associated with failure of potato to show
any evidence of being weedy or
invasive. The experts that EPA
consulted agree that it is not very likely
that potato would become feral or easily
spread into non-crop areas if it acquired
transgenic virus resistance. For
example, one expert consulted indicated
that ‘‘[t]he basis of poor survival of
cultivars in natural habitats is not due
to virus susceptibility’’ (Ref. 42). EPA
therefore believes that potato meets the
conditions recommended by the 2005
SAP for inclusion on the list and will
present low risk with respect to
weediness.
y. Soybean. EPA proposes that
soybean (Glycine max) be included on
the list in § 174.27(a)(1) based on
literature that is available on soybean
biology, the OECD Consensus Document
on the Biology of Glycine max (L.) Merr.
(Soybean) (Ref. 50), and EPA
consultations with soybean experts.
This body of information indicates that
soybean meets the three conditions
outlined above by the SAP: It does not
have wild or weedy relatives in the
United States with which it can form
viable hybrids in nature, it is not
currently weedy or invasive in the
United States, and there is no reason to
believe that acquisition of virus
resistance would make soybean weedy
or invasive, as viruses are not
consistently associated with failure of
soybean to show any evidence of being
weedy or invasive. All four experts
contacted by EPA indicated agreement
with these statements. For example, one
expert stated, ‘‘Acquiring transgenic
virus resistance will not change the
ability of soybean to become feral since
it will still be a domesticated species
and does not have the attributes to
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survive without human intervention.
Virus diseases in the U.S. do not
generally cause major yield loses [sic]
and resistance to some viruses is very
common in soybean. Transgenic virus
resistance will not substantially change
how the soybean interacts with most
environments’’ (Ref. 42). According to
the OECD consensus document, ‘‘[t]he
soybean plant is not weedy in character.
In North America, Glycine max is not
found outside of cultivation. In
managed ecosystems, soybean does not
effectively compete with other
cultivated plants or primary colonizers’’
(Ref. 50). EPA therefore believes that
soybean meets the conditions
recommended by the 2005 SAP for
inclusion on the list and will present
low risk with respect to weediness.
z. Starfruit. EPA proposes that
starfruit (Averrhoa carambola) be
included on the list in § 174.27(a)(1)
based on EPA consultations with
starfruit experts. These consultations
indicate that starfruit meets the three
conditions outlined above by the SAP.
One, it does not have wild or weedy
relatives in the United States with
which it can form viable hybrids in
nature. One expert mentioned that
starfruit can hybridize with wild
Averrhoa carambola, but another expert
indicated that researchers have
concluded wild starfruit trees can no
longer be found in the United States
(Ref. 42). Second, these experts agreed
that starfruit is not currently weedy or
invasive in the United States. Third,
these experts agreed that it is unlikely
that acquisition of virus resistance
would make starfruit weedy or invasive.
For example, one expert stated, ‘‘It is
highly unlikely that starfruit with
acquired transgenic resistance would
spread to non-crop areas because... seed
recalcitrance in starfruit... results in a
loss of viability shortly after harvest’’
(Ref. 42). EPA therefore believes that
starfruit meets the conditions
recommended by the 2005 SAP for
inclusion on the list and will present
low risk with respect to weediness.
aa. Sugarcane. EPA proposes that
sugarcane (Saccharum officinarum) be
included on the list in § 174.27(a)(1)
based on EPA consultations with
sugarcane experts. These consultations
indicate that sugarcane meets the three
conditions outlined above by the SAP.
One, it does not have wild or weedy
relatives in the United States with
which it can form viable hybrids in
nature. According to one expert,
‘‘Although in theory it should happen in
more tropical regions of the world,
hybrid seedlings among commercial or
wild relatives are not observed. Breeders
routinely generate hybrids among
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commercial sugarcane (derived from
interspecific hybrids of Saccarhum [sic]
officinarum and S. sponteneum), and
among commercial and wild relatives
(S. spontaneum mostly) under
controlled conditions of heating and
photoperiod control. The resulting
progeny are quite weak and must be
husbanded under greenhouse-type
conditions prior to planting in the field’’
(Ref. 42). Second, these experts agreed
that sugarcane is not currently weedy or
invasive in the United States. One
expert stated, ‘‘Commercial sugarcane is
clonally propagated. Occasionally some
of the harvested cane may be lost from
the trucks or wagons while in transport
from the field to the processing factory.
If the cane has not been burned prior to
harvest, volunteer plants occasionally
grow along the transport route. This
cane is not sexually reproducing, nor is
it invasive in nature. Simple roadside
mowing or natural weather conditions
usually eliminate it’’ (Ref. 42). Third,
these experts agreed that it is unlikely
that acquisition of virus resistance
would make sugarcane weedy or
invasive. For example, one expert
stated, ‘‘commercial sugar does not
become a feral pest under regular
commercial production conditions. The
majority of existing commercial
cultivars have been bred for genetic
resistance to various disease-causing
sugarcane viruses. None of these
cultivars have become feral or a pest in
anyway [sic]’’ (Ref. 42). EPA therefore
believes that sugarcane meets the
conditions recommended by the 2005
SAP for inclusion on the list and will
present low risk with respect to
weediness.
bb. Tulips. EPA proposes that tulips
(Tulipa spp.) be included on the list in
§ 174.27(a)(1) based on EPA
consultations with tulip experts. These
consultations indicate that tulips meet
the three conditions outlined above by
the SAP. One, they do not have wild or
weedy relatives in the United States
with which they can form viable
hybrids in nature. Two, they are not
currently weedy or invasive in the
United States, although two experts
indicated that Tulipa sylvestris
naturalizes in certain areas without
being viewed as a significant problem
because it reproduces only vegetatively.
Three, there is no reason to believe that
acquisition of virus resistance would
make tulips weedy or invasive. One
expert noted that this was ‘‘possible, but
unlikely. Virus resistance could
conceivably increase the vigor of the
vegetative spread of T. sylvestris’’ (Ref.
42). However, three other experts
believed that this was highly unlikely to
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occur. One said, ‘‘The need for chilling
in this genus means that it is restricted
to temperate areas with summer-cool
climates. Areas where it can persist are
very limited and there is a high degree
of browsing of this genus by vertebrates
such as deer that make seed production
in the wild a very rare occurrence in
nature in the U.S.’’ (Ref. 42). EPA
therefore believes that tulips meet the
conditions recommended by the 2005
SAP for inclusion on the list and will
present low risk with respect to
weediness.
ii. Adding plants to the categorical
exemption criterion in § 174.27(a)(1). As
the Agency gains additional experience,
it may propose to add crops to the list.
In addition, any person may petition the
Agency to add particular crops to the
list. EPA would evaluate any potential
candidates against the same
considerations used in this rulemaking
to develop the list in § 174.27(a)(1)
discussed above. Consequently, for a
petition to be successful, it should
contain sufficient data or other
information to allow EPA to perform
such an analysis, e.g., published
information or a consensus opinion
among experts in the particular crop
that addresses the questions EPA posed
in its expert consultations (discussed in
Unit III.C.2.i.). Petitioners are welcome
to consult with EPA prior to preparing
a submission to discuss the information
that would be required. EPA would
consult with USDA in evaluating
petitions for adding plants to
§ 174.27(a)(1).
Any subsequent addition of crops to
the list in § 174.27(a)(1), either through
the Agency’s own initiative or in
response to a petition from the public,
may only occur through rulemaking.
Under FIFRA section 25, rulemaking
involves several steps, including
reviews by the SAP and USDA. In
general, EPA would seek to expedite the
process and proceed through direct final
rulemaking where feasible. Under such
a process, in cases where EPA believes
that the proposal will not raise
scientifically complicated issues, EPA
would simultaneously issue a final rule
and a proposal. If no adverse comments
were received, the final rule would go
into effect and EPA would withdraw the
proposed rule. In the event of adverse
comment, EPA would withdraw the
final rule and would proceed to issue a
final rule that addressed the public
comments received on the proposal. In
addition, as part of this current
rulemaking, because EPA’s analysis to
determine whether to add a crop to the
list would be consistent with the criteria
provided by the SAP, the Agency would
request that the SAP generally waive its
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review of subsequent rules seeking to
add further crops to the list in
§ 174.27(a)(1) unless EPA subsequently
determines that a particular rule raised
novel or particularly complex scientific
issues.
iii. Proposed exemption criterion
conditional on Agency determination in
§ 174.27(a)(2). EPA recognizes that
many PVCP-PIP/plant combinations
would reasonably be expected to pose
low risk with respect to weediness even
though the crop plant containing the
PVCP-PIP is not on the Agency’s
proposed list in § 174.27(a)(1). EPA has
not conducted an exhaustive survey of
all crop plants to evaluate them for
inclusion on this list and therefore
recognizes that additional plants may
meet the conditions that were used to
compile this list of plants. Therefore, in
addition to the categorical exemption
criterion, EPA also believes that a
criterion conditional on Agency
determination could be developed that
would identify plants that are low risk
with respect to weediness.
EPA is considering four options for
such a conditional exemption criterion
under which PVCP-PIP/plant
combinations that fail to meet
§ 174.27(a)(1) could still meet
§ 174.27(a) under § 174.27(a)(2), subject
to an Agency review. Each of the
options reflects a somewhat different
approach to implementing the
recommendations of the 2005 SAP (Ref.
11). EPA does not currently have a
preferred approach and presents several
options to promote full consideration of
the issues, although option 1 is
presented in the regulatory text so the
public could see how § 174.27(a)(2)
might fit into the overall framework of
the exemption.
a. Option 1. The first option for
§ 174.27(a)(2) provides the strictest
interpretation of the 2005 SAP advice.
Under this option, a PVCP-PIP would
meet § 174.27(a) under § 174.27(a)(2) if
the Agency determines after review that
the plant containing the PIP meets all of
the following:
(i) Has no wild or weedy relatives in the
United States with which it can form viable
hybrids in nature.
(ii) Is not a weedy or invasive species
outside of agricultural fields in the United
States.
(iii) Is unlikely to establish weedy or
invasive populations outside of agricultural
fields in the United States even if the plant
contains a PVCP-PIP.
EPA would expect exemption
submissions to document that the plant
meets these conditions in the opinion of
agronomists, breeders, ecologists, and
other experts working with the specific
taxa in question or based on data. When
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these conditions are met, the likelihood
that a PVCP-PIP could cause increased
weediness of any plant would be very
small, as discussed in the following
paragraphs.
If the plant containing the PVCP-PIP
has no wild or weedy relatives in the
United States with which it can form
viable hybrids in nature and thus would
meet the criterion in § 174.27(a)(2)(i)
under option 1, it would not be possible
for the PVCP-PIP to inadvertently be
transferred to any wild or weedy
relatives, e.g., through pollen flow.
Whether the recipient plant ‘‘can
produce viable hybrids in nature’’ is a
critical attribute that would definitively
determine the potential for introgression
of the PVCP-PIP into a native or
naturalized plant population. Although
hybrids must be able to reproduce
themselves in order for introgression to
occur, the production of ‘‘viable’’
hybrids (i.e., those that are able to grow)
may be described more clearly in a
regulatory standard than examining the
reproductive potential of any hybrids. In
many cases, reproductive potential of
hybrids has not been fully investigated.
Given that reduced fertility in F1 cropwild hybrids is frequently restored to
normal in subsequent generations (Ref.
37), measurement of hybrid fertility
involves consideration of several
generations. In addition, viability is a
more reliable standard because even
very low rates of gene transfer could
lead to introgression (Ref. 51),
suggesting that any degree of hybrid
fertility could indicate the potential for
introgression to occur. As noted by the
2005 SAP, ‘‘it is known that favorable
alleles (including, perhaps, a PVCP-PIP)
can pass easily from one species to
another through hybrid zones, even
when the hybrids have very low fitness
(Barton 1986)’’ (Refs. 11 and 52). The
Agency recognizes that introgression of
a trait such as virus resistance into
natural plant populations does not
automatically confer a competitive
advantage to the recipient population.
However, at this time, there is little
information available to predict
categorically whether acquisition of
such a trait might affect the
competitiveness of a specific plant
population, and the available
information does not allow the Agency
to make this determination a priori. The
ability to produce viable hybrids is
relatively easy to evaluate, resulting in
a clear criterion that ensures an effective
limitation on the potential for
introgression. Such language also
clarifies that the relevant question is
whether the hybrid can be produced ‘‘in
nature.’’ The fact that plants could be
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crossed in the laboratory or greenhouse
is not necessarily indicative of a plant’s
true reproductive potential. The
Agency’s focus is whether a viable
hybrid could be produced under normal
growing conditions in the field or in
nature, rather than under controlled
experimental conditions that might have
little relevance to behavior in the
environment.
If the plant containing the PVCP-PIP
is not a weedy or invasive species
outside of agricultural fields in the
United States and thus would meet the
criterion in § 174.27(a)(2)(ii) under
option 1, established and persistent feral
populations of the crop presenting
difficult management issues in natural
or semi-managed ecosystems would be
unlikely. Thus, transfer of the PVCP-PIP
from the crop to a feral population
would be unlikely to exacerbate what
could already be a difficult problem by
inadvertently increasing the
population’s weediness potential. EPA
proposes inclusion of the term ‘‘outside
of agricultural fields’’ to emphasize that
the key consideration is the plant’s
behavior in natural settings, including
semi-managed habitat surrounding
agricultural fields as opposed to its
behavior within the fields themselves.
EPA recognizes that most crops within
agricultural fields form volunteer
populations, where propagules of the
crop from the previous rotation grow in
the subsequent crop rotation. The
Agency believes the language ‘‘outside
of agricultural fields’’ appropriately
excludes this situation from
consideration.
If the plant containing the PVCP-PIP
is unlikely to establish weedy or
invasive populations outside of
agricultural fields in the United States
even if the plant contains a PVCP-PIP
and thus would meet the criterion in
§ 174.27(a)(2)(iii) under option 1, an
additional level of assurance would be
provided that the crop plant would not
present weediness concerns through
acquisition of a PVCP-PIP. EPA believes
that this condition could in general be
met based on the opinion of experts on
the particular crop. Experts may judge,
for example, that acquisition of virus
resistance is unlikely to change the
weedy or invasive characteristics of the
plant if the crop does not appear to be
weedy or invasive when virus infection
is known to be absent from a particular
area or over a particular period of time.
Available empirical data could be used
in the determination or may be gathered
if expert opinion cannot resolve the
question.
EPA proposes to define the term
‘‘weedy species’’ used in
§ 174.27(a)(2)(ii) to mean ‘‘a species that
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is an aggressive competitor in natural
ecosystems.’’ EPA intends to use the
term ‘‘invasive species’’ consistent with
the definition in Executive Order 13112,
meaning an alien species whose
introduction causes or is likely to cause
economic or environmental harm or
harm to human health. An alien species
means, with respect to a particular
ecosystem, any species, including its
seeds, eggs, spores, or other biological
material capable of propagating that
species, that is not native to that
ecosystem. EPA uses the phrase ‘‘weedy
or invasive populations’’ in
§ 174.27(a)(2)(iii) consistent with these
definitions.
EPA notes that the criterion in
§ 174.27(a)(2)(i) under option 1 does not
necessarily strictly hold for every crop
that appears on the list in proposed
§ 174.27(a)(1). In some cases, EPA was
able to make a low risk determination
for a particular crop, e.g., corn, in spite
of the possible presence of wild or
weedy relatives in the United States
with which the plant may in rare cases
form viable hybrids in nature. EPA has
presented the basis for such conclusions
in this proposed rule, and the public
can clearly understand why the crops in
§ 174.27(a)(1) meet the Agency’s low
risk standard with respect to weediness
concerns. Given that several crops for
which EPA has made a low risk
determination and proposes to include
in § 174.27(a)(1) would not meet
§ 174.27(a)(2) as proposed under option
1, EPA believes that option 1 may be too
narrow. Accordingly, EPA is
considering other options for
§ 174.27(a)(2) that are based on a less
literal interpretation of the SAP’s
recommendations but which the Agency
believes are nevertheless consistent
with the SAP’s intent.
b. Option 2. The second option EPA
is considering is that a PVCP-PIP would
meet the criterion in § 174.27(a)(2)(i) if
‘‘the plant containing the PIP has no
wild or weedy relatives in the United
States with which it can form viable,
fertile hybrids in nature, or if fertile, the
resulting hybrid cannot establish
populations in the environment.’’ EPA
is considering this option because most
crops are able to form viable hybrids
with a wild or weedy relative in some
part of the United States. However,
some viable, fertile hybrids may
nevertheless present low risk with
respect to concerns associated with
weediness, e.g., if the hybrids are weak
and lack the ability to establish. On the
other hand, fertility and the potential to
establish are more difficult
characteristics to evaluate than viability
because many more variables affect the
determination, suggesting that it might
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be more appropriate in these cases for
the Agency to require that data be
collected for a period of time after
commercial deployment that could
confirm the Agency’s original analysis.
However, while such conditions may be
readily placed on a PVCP-PIP
registration, they could not be placed on
an exempt PVCP-PIP. In addition,
determinations under option 2 would be
more difficult for the public to predict
than determinations under option 1, as
discussed in Unit III.A.2.
c. Option 3. Under the third option
being considered, EPA would adopt
only the criteria in § 174.27(a)(2)(i) and
(a)(2)(ii) as discussed above under
option 1. The rationale for such an
approach is that it may not be necessary
to evaluate the criterion in
§ 174.27(a)(2)(iii) in order to make a low
risk determination because the issues
are adequately addressed by the other
two criteria. Viruses generally do not
uniformly affect crops every season in
every place they are planted - even
those crops that viruses significantly
impact such that development of a
PVCP-PIP to combat the disease might
be undertaken. Crops will thus have
repeated opportunity to escape
cultivation in seasons and in areas
where there is no virus infestation. If
weedy tendencies are rarely or never
observed in any part of the crop’s range,
it is unlikely that virus resistance affects
the crop’s ability to escape cultivation
and establish weedy populations.
Unlike wild or weedy plant relatives
that may at times be infected by viruses
and may be negatively impacted by
viruses in ways that are not obvious to
untrained observers, breeders and
farmers are intimately aware of the type
of damage done by virus infection to
crops and are therefore well aware when
their fields are or are not infected. Crop
plants have been observed under a
diverse range of environmental
conditions over many years. If a PVCPPIP were likely to make a crop weedy
or invasive, such tendencies would
likely have been observed even without
virus resistance at some point in time
given the level of observation crops
generally receive due to the necessity to
actively manage their cultivation. Such
crops showing weedy or invasive
tendencies would not meet the criterion
in § 174.27(a)(2)(ii), suggesting that the
criterion in § 174.27(a)(2)(iii) is largely
redundant with this condition.
EPA notes that option 3 is likely to be
equally as narrow as options 1 and 2.
The advantage of the option would be
a simplification of the issues that a
PVCP-PIP developer would need to
address as part of a submission for an
exemption determination.
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EPA could consider factors that are
not considered under options 1–3 but
that would affect the potential impact of
PVCP-PIP acquisition as part of
evaluating a PVCP-PIP for FIFRA
registration. For example, EPA could
take into account the effect of virus
infection on such species, the existence
and impact of any natural virus
resistance in the population, the overlap
of the plant’s distribution with crop
cultivation areas, and other relevant
considerations.
d. Option 4. The fourth option EPA is
considering is that a PVCP-PIP would
meet § 174.27(a)(2) if the Agency
determines that ‘‘the PVCP-PIP is
unlikely to significantly change the
population size or distribution of the
species containing the PVCP-PIP outside
of agricultural fields or the population
size or distribution of any wild or
weedy species in the United States that
could acquire the PVCP-PIP through
gene transfer.’’ EPA is considering this
fourth option because the Agency
recognizes that many PVCP-PIPs
excluded from exemption under the
criterion in § 174.27(a)(2)(i) of options
1–3 because of wild or weedy relatives
in the United States may nevertheless
present low risk. The presence of wild
or weedy relatives relates only to
potential exposure of the PVCP-PIP and
does not indicate whether the PVCP-PIP
is likely to cause any adverse effects
even if it were to transfer to these
relatives. EPA believes that such an
evaluation would be consistent with the
advice of the 2005 SAP, which noted
that ‘‘[t]he probability that a particular
transgene will lead to increased
weediness depends on the phenotype
conferred by the transgene and on the
ecological factor(s) currently limiting
the size or distribution of the wild
species. In particular, if the transgene
alters plant response to an ecological
factor limiting population size, then
population dynamics may be affected.
For PVCP-PIPs, the relevant
consideration is whether virus
resistance (conferred by the PVCP-PIP)
leads to changes in the size or
distribution of wild plant species with
the PVCP-PIP’’ (Ref. 11).
With option 4, EPA would conduct a
risk assessment to evaluate a clear end
point - whether there is likely to be a
significant change in the population size
or distribution of the species containing
the PVCP-PIP outside of agricultural
fields or the population size or
distribution of any wild or weedy
species in the United States that could
acquire the PVCP-PIP through gene
transfer. However, for the vast majority
of species, many characteristics that
would influence this determination are
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currently poorly understood, e.g., the
impact of virus infection on wild plant
populations and the likely selective
advantage afforded by acquisition of
virus resistance. As a result, both the
nature of EPA’s evaluation and the type
and extent of data that might need to be
provided to the Agency resemble much
more closely what would be required to
evaluate weediness issues during a
FIFRA registration review. In addition,
the more the exemption determination
process resembles a full risk assessment,
the longer the time required for EPA to
complete such a review.
Although EPA would seek public
comment on determinations that a
PVCP-PIP met § 174.27(a)(2) according
to the procedure for exemptions
utilizing any Agency-determined
criteria, Agency determinations may be
more controversial with this option than
with other options that have more
clearly defined criteria. EPA believes
that case-by-case determinations could
be made appropriately and that the data
requirements needed to evaluate the
criterion under option 4 would not
necessarily be overly burdensome. EPA
notes that in many cases much of the
data, if not all, needed for EPA to
evaluate a criterion such as this fourth
option would also be needed for a
petition for determination of
nonregulated status submitted to USDA.
EPA believes that the flexibility of this
option will make it more likely that the
Agency would identify the largest
number of low risk products that could
qualify for exemption.
For all options for proposed
§ 174.27(a)(2), the Agency believes the
entire United States is the relevant
scope of inquiry because the proposed
exemption would carry no limitations
on where the exempted PVCP-PIP/plant
combination could be planted and thus
could be planted in all areas subject to
U.S. law. FIFRA section 2(aa) defines
‘‘State’’ as ‘‘a State, the District of
Columbia, the Commonwealth of Puerto
Rico, the Virgin Islands, Guam, the
Trust Territory of the Pacific Islands,
and American Samoa. Accordingly, the
term ‘‘United States’’ used in this
proposal includes all these areas, and
EPA proposes to incorporate a
definition of ‘‘United States’’ paralleling
the FIFRA definition of ‘‘State’’ into the
definitions in 40 CFR 174.3.
As an alternative to Agency review
pursuant to § 174.27(a)(2), a developer
could petition EPA to add a crop to the
list in § 174.27(a)(1). In some cases, EPA
expects that the same data/information
that would support a determination that
a crop meets § 174.27(a)(2) would
support listing the crop in
§ 174.27(a)(1). However, because a plant
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can only be added to the list in
§ 174.27(a)(1) through rulemaking, EPA
expects that many developers will
instead prefer to obtain an Agency
determination under § 174.27(a)(2).
However, once a plant is added to the
list in § 174.27(a)(1), future PVCP-PIPs
used in that plant would meet
§ 174.27(a) without any Agency review.
3. Historical approaches. In 1994 EPA
proposed two different alternatives for
exempting PVCP-PIPs from FIFRA
requirements. The Agency prefers the
approaches discussed in the preceding
Subunit because they have been
developed based on recent interactions
with the SAP and thus represent the
most current science. One 1994
alternative contained exemption criteria
directed towards addressing concerns
associated with gene transfer to identify
those PVCP-PIP/plant combinations
with the lowest potential to confer
selective advantage on wild or weedy
plant relatives. EPA described this
alternative exemption as follows:
Coat proteins from plant viruses [would be
exempt] if the genetic material necessary to
produce a coat protein is introduced into a
plant’s genome and the plant has at least one
of the following characteristics:
(1) The plant has no wild relatives in the
United States with which it can successfully
exchange genetic material, i.e., corn, tomato,
potato, soybean, or any other plant species
that EPA has determined has no sexually
compatible wild relatives in the United
States.
(2) It has been demonstrated to EPA that
the plant is incapable of successful genetic
exchange with any existing wild relatives
(e.g., through male sterility, self-pollination).
(3) If the plant can successfully exchange
genetic material with wild relatives, it has
been empirically demonstrated to EPA that
existing wild relatives are resistant or
tolerant to the virus from which the coat
protein is derived or that no selective
pressure is exerted by the virus in natural
populations (59 FR 60504, November 23,
1994).
EPA carefully reconsidered this 1994
proposal in its deliberations for today’s
proposed exemption and presented
these criteria in modified form to the
FIFRA SAP at the October 2004 and
December 2005 meetings for
consideration. In light of comments
received from the FIFRA SAP and
additional scientific information
available since 1994, EPA no longer
believes this alternative would
adequately address questions associated
with weediness in a manner that could
be reasonably implemented. However,
EPA still considers that it would be
appropriate to limit the exemption
based on the concerns outlined in the
earlier proposal associated with
acquisition of virus resistance through
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hybridization with a transgenic plant
containing a PVCP-PIP.
Although similar in intent to
characteristic (1) of this option proposed
in 1994, today’s proposed criterion in
§ 174.27(a)(2)(i) under option 1 focuses
in part on the potential to ‘‘form viable
hybrids in nature’’ rather than simply
‘‘exchange genetic material’’ because the
former is a clearer standard for
determining whether a PVCP-PIP could
have the potential to affect a recipient
plant population negatively. The ability
to exchange genetic material, which is
often demonstrated by performing hand
crosses in the laboratory or greenhouse,
may not indicate any relevant
information about how the plants would
behave in nature. Today’s proposed
criterion in § 174.27(a)(1) also uses a
somewhat different list of plants than
the four in the 1994 proposal. Several
species have been added (see Unit
III.C.2.i.) and tomato has been removed
from the list because of information
acquired through expert consultation.
(See Unit VII for a discussion of this
information and to read EPA’s request
for comment). When EPA presented a
criterion similar to the first
characteristic in the 1994 proposal to
the 2004 SAP, they responded that ‘‘the
Panel was of the opinion that the
absence of a competent wild/weedy
relative positioned in relation to the
plant containing the PVCP-PIP was an
appropriate condition.’’ The 2005 SAP
also ‘‘was supportive of the Agency’s
intent to exempt from regulation any
PVCP-PIP crops that (1) do not have
sexually compatible wild relatives in
the location of intended cultivation (US
& Territories) and (2) are not likely to
become weedy themselves’’ (Ref. 11).
EPA now also believes that
characteristic (2) of the option proposed
in 1994 may be insufficient based on the
conclusions of the 2004 SAP and the
National Research Council that current
methods of bioconfinement are
imperfect and are unlikely to adequately
restrict gene flow (Refs. 25 and 53). The
Agency asked the 2004 SAP whether the
condition that ‘‘genetic exchange
between the plant into which the PVCPPIP has been inserted and any existing
wild or weedy relatives is substantially
reduced by modifying the plant with a
scientifically documented method, (e.g.,
through male sterility)’’ would be
necessary and/or sufficient to minimize
the potential for a PVCP-PIP to harm the
environment through gene transfer from
the crop plant containing the PVCP-PIP
to wild or weedy relatives. The Panel
‘‘accepted that tactics aiming at
diminished gene exchange are highly
desirable and even necessary but are not
sufficient’’ (Ref. 25).
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In spite of such concerns, EPA is still
considering whether a criterion
involving biocontainment could be
sufficient to enable the Agency to
determine with review that a product
presents low risk with respect to
concerns associated with weediness.
The 2005 SAP concluded ‘‘that if highly
effective biological containment and
biological mitigation methods could be
deployed concurrently with the PVCPPIP, then it would be possible to exempt
crops with sexually compatible wild
relatives. This opinion is different from
the opinion of the October 2004 FIFRA
SAP. The [2005] Panel concluded that
this difference is probably due to
advances in containment and mitigation
strategies. For this reason, exemptions
might be granted to any crop that
hybridizes with a wild relative in the
US, its possessions or territories, if the
F1 and BC (backcross) hybrids have very
low fitness such that it is effectively
lethal. Additionally, an exemption
might be possible if specific genes for
lowering fitness are in tandem
constructs with the PVCP-PIP gene in
such a way that they cannot readily
segregate from each other. The Panel did
not determine what level of
effectiveness would be required but, it
was agreed that stacked strategies would
reduce the cumulative risk, and should
be strongly considered’’ (Ref. 11).
Bioconfinement strategies are known
to have a wide range of efficacy, and no
standard level of efficacy to ensure
environmental safety has been
determined (Ref. 53). Additionally,
some techniques may introduce risk
concerns that must be evaluated, e.g.,
unintended impacts on wildlife that eat
seeds or pollen (Ref. 25). However,
scientific advancements may make
bioconfinement techniques sufficiently
reliable and safe in the future such that
deployment with a PVCP-PIP would be
sufficient to reach a low risk finding
with respect to concerns associated with
weediness (Refs. 54 and 55). Therefore,
EPA is still considering a condition
such as characteristic (2) proposed in
1994 that would constitute an
alternative way to meet § 174.27(a)(2)
under any of the options discussed in
this Preamble. For example,
§ 174.27(a)(2) might read:
The Agency determines after review that
the plant containing the PIP:
(i) Has no wild or weedy relatives in the
United States with which it can form viable
hybrids in nature or employs a highly
effective biological containment technique.
(ii) Is not a weedy or invasive species
outside of agricultural fields in the United
States or employs a highly effect
biomitigation construct that ensures escapes
from cultivation are too unfit to compete
with wild-types.
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EPA believes that characteristic (3) of
the option proposed in 1994 is sound
conceptually. However, the Agency’s
intent in developing this exemption has
historically been to have criteria that
identify low risk PVCP-PIPs such that
the criteria could be evaluated with
information that a developer is likely to
have acquired in the course of
developing the product and not require
significant data generation. The Agency
presented a similar criterion to the 2004
SAP for their consideration: ‘‘all
existing wild or weedy relatives in the
United States with which the plant can
produce a viable hybrid are tolerant or
resistant to the virus from which the
coat protein is derived.’’ The Panel
members suggested that such a criterion
would be difficult to implement in a
clear and transparent exemption review
process given that ‘‘[t]he Panel had
particular difficulty when attempting to
add precision to approaches that should
be followed when sampling wild and
weedy relatives for the occurrence of
specific virus tolerance or resistance as
specified by the Agency.’’
As an alternative to a criterion like
that described by characteristic (3) in
the 1994 proposal whose evaluation
would necessitate collection of
potentially significant amounts of data,
EPA presented another option to the
2005 SAP: ‘‘(i) the plant containing the
PVCP-PIP is itself not a weedy or
invasive species outside of agricultural
fields in the United States, its
possessions, or territories, and (ii) the
plant containing the PVCP-PIP does not
have relatives outside of agricultural
fields in the United States, its
possessions, or territories that are weedy
or invasive species or endangered/
threatened species with which it can
produce viable hybrids in nature’’ (Ref.
11). However, the Panel concluded that
‘‘the probability that a particular
transgene alters the dynamics of a wild
relative cannot be predicted by the
current status of the wild species as
weedy, invasive, or threatened/
endangered. The Panel agreed that the
criteria proposed by the Agency would
not correctly identify PVCP-PIPs which
pose unacceptable environmental risks’’
(Ref. 11). EPA has therefore concluded
that the Agency is unable at this time to
articulate a clear criterion for exemption
that would expand the eligible plants
beyond those roughly described by the
ideas in the 1994 characteristic (1)
unless the Agency were to adopt a
criterion whose evaluation involved
conducting a risk assessment of the
PVCP-PIP/plant combination such as it
put forth in this preamble as the fourth
option for proposed § 174.27(a)(2), i.e.,
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that the PVCP-PIP is unlikely to
significantly change the population size
or distribution of the species containing
the PVCP-PIP outside of agricultural
fields or the population size or
distribution of any wild or weedy
species in the United States that could
acquire the PVCP-PIP through gene
transfer (discussed in Unit III.C.2.iii.d.).
The other alternative proposed in
1994 did not contain a criterion
addressing concerns associated with
gene flow. This option proposed a full
categorical exemption for all PVCP-PIPs
(59 FR 60503). This option is no longer
the Agency’s preferred approach for a
number of reasons. Specifically, EPA
has received scientific advice since
issuance of the 1994 proposal calling
into question the Agency’s 1994
rationale that all PVCP-PIPs meet the
FIFRA 25(b)(2) exemption standard,
including gene flow considerations.
Although EPA believes that many
PVCP-PIPs present low risk and thus
meet the FIFRA 25(b)(2) exemption
standard, in order to categorically
exempt all PVCP-PIPs, the Agency must
be able to draw this conclusion for all
PVCP-PIPs. Advances in scientific
understanding since 1994 suggest it may
not be possible to support this rationale
for all PVCP-PIPs and that certain PVCPPIPs may pose a greater level of risk
than is characteristic of the group as a
whole. For example, virus resistance is
common in natural plant populations as
evidenced by conventionally bred virus
resistant plants that are only possible
due to naturally existing resistance in
crop and wild relative populations (Ref.
20). This fact suggests that acquisition of
virus resistance is often unlikely to
introduce a novel trait into many plant
populations. However, some notable
exceptions to the ubiquity of virus
resistance in natural plant populations
exist including the lack of successful
conventionally bred resistance to barley
yellow dwarf virus in major crops and
the lack of natural resistance in some
wild relatives of these crops (Ref. 36).
Such information suggests that
acquisition of a PVCP-PIP by such wild
relatives of these plants has the
potential to free these wild relatives
from what may be an important
ecological constraint. The conclusions
of the 2004 FIFRA SAP are consistent
with the idea that it may not be possible
to apply a general exemption rationale
to all PVCP-PIPs. The report concluded
that ‘‘...PVCP-PIPs [have] no inherent
capacity to harm the environment.’’
However, ‘‘[i]t was recognized that
knowledge of hybridization potential
was sparse and of very unequal quality
but the likelihood of serious economic
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harm was such that some plants
engineered to contain stress tolerant
traits should not be released’’ (Ref. 25).
The 2005 SAP’s conclusions discussed
above also clearly suggest that crops
containing a PVCP-PIP that have wild
relatives must be carefully considered
on a case-by-case basis (Ref. 11).
Similarly, the 2000 National Research
Council (NRC) report recommended that
because of concerns associated with
hybridization with weedy relatives,
‘‘EPA should not categorically exempt
viral coat proteins from regulation
under FIFRA. Rather, EPA should adopt
an approach, such as the agency’s
alternative proposal..., that allows the
agency to consider the gene transfer
risks associated with the introduction of
viral coat proteins to plants’’ (Ref. 10).
D. Viral Interactions
1. Scientific issues. In addition to
weediness, a key issue associated with
PVCP-PIPs is the question of whether
they could affect the epidemiology and
pathogenicity of plant viruses. Given the
potential impact of virus infection, such
changes might affect competitiveness of
plant populations thereby altering
ecosystem dynamics, e.g., through
significant changes in species
composition of populations, resource
utilization, or herbivory.
The genetic material of plant viruses
may be composed of either RNA or
DNA, although most have RNA genomes
(Ref. 56). Although there are significant
differences between RNA and DNA
viruses, both are obligate parasites that
usually move from plant to plant via
vector-mediated transmission. Such
transmission, in connection with other
types of virus transmission, commonly
leads to mixed viral infections in crops
and other plants (Ref. 57). In natural,
mixed infections, viral genomes from
different strains and/or different species
simultaneously infect the same plant
and thus have opportunities to interact
(e.g., through recombination,
heterologous encapsidation, or synergy).
In spite of many opportunities for
interaction in nature, such events rarely
lead to any detectable adverse outcome
(Ref. 58). However, such in planta
interactions have the potential to result
in a virus that causes increased
agricultural or other environmental
damage.
In transgenic plants containing PVCPPIPs, every virus infection can be
considered in one sense to be a mixed
infection with respect to the coat
protein gene (Ref. 59). The key
questions facing EPA are whether
interactions between such introduced
plant virus sequences and infecting
viruses in transgenic plants may
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increase in frequency or be unlike those
expected to occur in nature (Ref. 60).
The Agency has written a literature
review addressing these questions (Ref.
60) and will briefly describe the issues
associated with recombination,
heterologous encapsidation, and
synergy below. EPA provides a general
overview of each of the processes
separately, followed by a brief review of
relevant field studies that investigated
these processes.
i. Recombination. Recombination is a
natural process that can occur during
replication of DNA or RNA whereby
new combinations of genes are
produced. Plant virus recombination
can occur between members of the same
virus pathotype in natural infections,
contributing to the number of variants
that exist within that pathotype.
Recombination can also occur when
different viruses coinfect the same plant
and interact during replication to
generate virus progeny that have genetic
material from each of the different
parental genomes. Although
recombination likely occurs regularly in
mixed viral infections, recombination
only rarely leads to viable viruses and
even more rarely to viruses with truly
novel behavior and/or characteristics or
any detectable adverse outcome. In
order to persist in nature, a recombinant
virus must be competitive with variants
of the parental viruses that have already
demonstrated success in all stages of the
infective cycle, e.g., transmission, gene
expression, replication, and assembly of
new virions (Ref. 58). An analysis of
cucumber mosaic virus (CMV) isolates
in natural populations showed that
viable recombinants were very rarely
recovered in mixed infections (Ref. 61).
Although selection in the field
appears to act against persistence of
new, recombinant viruses,
recombination is thought to play a
significant role in virus evolution,
presumably because recombinant
viruses are on very rare occasions able
to outcompete existing viruses. How a
virus with increased pathogenicity or
altered epidemiology might conceivably
be created through recombination was
suggested by a laboratory experiment in
which a pseudorecombinant strain was
created by experimentally combining
regions of the CMV and tomato aspermy
virus (TAV) genomes. This artificially
manipulated virus was found to cause
more severe symptoms than either of the
parental genomes, although the
recombinant was not a fully-functional
virus as it was not able to move beyond
the initially infected cells (Ref. 62) and
would therefore not be expected to
persist in nature. Another laboratory
experiment has shown interspecific
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recombination between CMV and TAV
under conditions in which
recombinants would not be expected to
have any particular fitness advantage
(Ref. 63). In another example, alteration
of the host range of tobacco mosaic virus
(TMV) occurred when a chimeric virus
expressed the coat protein from alfalfa
mosaic virus (AMV) instead of its own
(Ref. 64).
Evidence of past recombination
having led to the creation of new RNA
viruses has been documented in a
number of different groups including
bromoviruses (Ref. 65), luteoviruses
(Ref. 66), nepoviruses (Ref. 67), and
cucumoviruses (Ref. 68). Sequence
analysis of viruses from the family
Luteoviridae indicated that this family
has evolved via both intra- and
interfamilial recombination (Ref. 69).
Interspecific recombination between
two related potyviruses, soybean mosaic
virus (SMV) and bean common mosaic
virus (BCMV) apparently led to the
creation of watermelon mosaic virus
(WMV) with a broader host range than
either SMV or BCMV (Ref. 70). Whereas
these latter two viruses are generally
restricted to Leguminosae, WMV has
one of the broadest host ranges among
the potyviruses being able to infect both
monocots and dicots. For RNA viruses,
evidence of recombinant viruses arising
in recent history has not been reported,
suggesting that recombination as a factor
in RNA virus evolution may generally
only be significant over a longer
timescale.
Recombination has also played a role
in the evolution of new DNA viruses
including caulimoviruses (Ref. 71) and
geminiviruses (Refs. 72 and 73). For
DNA viruses, geminiviruses in
particular, several instances can also be
cited in which relatively recent
recombination events appear to have
resulted in the creation of new viruses.
For example, a recent epidemic of
severe cassava mosaic disease in
Uganda is thought to be due to the
combination and/or sequential
occurrence of several phenomena
including recombination,
pseudorecombination, and/or synergy
among cassava geminiviruses (Ref. 72).
It also appears that tomato-infecting
begomoviruses that have emerged in the
last 20 years around the Nile and
Mediterranean Basins probably resulted
from numerous recombination events
(Ref. 74). In addition, a natural
recombinant between tomato yellow leaf
curl Sardinia virus and tomato yellow
leaf curl virus was detected in southern
Spain with a novel pathogenic
phenotype that might provide it with
selective advantage over the parental
genotypes (Ref. 75). Finally, analysis of
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a newly described Curtovirus species
associated with disease of spinach in
southwest Texas suggests that it may be
the result of recombination among
previously described Curtovirus species
(Ref. 76).
In addition to virus-virus
recombination, recombination has also
been found to occur between virus and
plant host RNA. Sequence analysis of
the 5’ terminal sequence of potato
leafroll virus (PLRV) suggests that it
arose via recombination with host
mRNA (Ref. 77). Evidence suggests that
such recombination events can affect
virus virulence (for review see Ref. 78).
Like a plant host genome, transcripts of
viral transgenes would be available for
recombination with infecting viruses,
and portions of the transgene could thus
be incorporated into the replicating
virus. Several laboratory experiments
have investigated the potential for
recombination between viral transgenes
and infecting viruses of the same
species. These experiments show that
recombination can occur between viral
transgenes and both RNA viruses (Refs.
79, 80, 81, 82, and 83) and DNA viruses
(Refs. 84, 85, 86, and 87). However, the
relevance to PVCP-PIPs of the latter
experiments with DNA viruses is
unclear because the transgenic plants
used in the experiments actually show
no viral resistance; attempts to develop
transgenic DNA virus-resistant plants in
general have had little success (Ref. 57).
In addition, to facilitate the detection of
recombinants, most of these
experiments were conducted under
conditions of high selective pressure
favoring the recombinant, i.e., only
recombinant viruses were viable. The
selective pressure under normal field
conditions would likely favor the
parental viruses rather than a
recombinant as parental viruses will be
competent in all of the functions needed
for propagation and will outnumber the
new recombinant.
ii. Heterologous encapsidation.
Heterologous encapsidation occurs
when the coat protein subunits of one
virus surround and encapsidate the viral
genome of a different virus. The coat
protein, possibly in conjunction with
other viral factors, is often essential for
transmission and responsible for
conferring the high degree of vector
specificity. Therefore, a heterologously
encapsidated viral genome may be
transmitted by the vectors of the virus
contributing the coat protein rather than
the vectors of the virus contributing the
viral genome. For many viruses,
transmission from plant to plant occurs
by insect vectors, and each virus tends
to be transmitted by only one type of
insect (Ref. 1). To the extent that vectors
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visit different groups of plants, vectors
carrying a heterologously encapsidated
viral genome may carry it to a plant the
virus does not normally encounter (Ref.
59).
Most evidence of heterologous
encapsidation is derived from laboratory
or greenhouse studies. Even though
there is a high frequency of mixed
infections in nature, most mixed
infections do not lead to heterologous
encapsidation, and those virus
interactions that do occur tend to be
very specific rather than random
interactions between unrelated viruses
(Ref. 88). Only among some types of
plant viruses is heterologous
encapsidation regularly observed. Its
frequency depends on the relationship
between the viruses involved, being
more likely to occur among closely
related viruses (Ref. 89). An expansion
of aphid vector specificity due to
heterologous encapsidation was first
observed in plants infected with two
different isolates of barley yellow dwarf
virus (BYDV; Ref. 90) and was later
shown to be a general phenomenon
among these viruses in natural
populations of several plant species
(Ref. 91). Heterologous encapsidation
was also shown to occur in potyviruses.
An isolate of zucchini yellow mosaic
virus (ZYMV) that is normally nonaphid transmissible due to a
transmission-deficient coat protein was
found to be transmitted by the aphid
vector due to heterologous
encapsidation when in a mixed
infection with another potyvirus,
papaya ringspot virus (Ref. 92).
Heterologous encapsidation is essential
for movement of some viruses. For
example, umbraviruses do not encode a
coat protein, and therefore transmission
between plants occurs through
encapsidation by an aphid-transmissible
luteovirus coat protein (Ref. 93).
Heterologous encapsidation is
considered a possible environmental
concern associated with PVCP-PIPs
because of the potential that if a virus
is heterologously encapsidated by a
PVC-protein, the viral genome might be
able to spread to plants the virus
ordinarily had no means of reaching and
thus could not have infected.
Experimental studies have shown that
some PVC-proteins in transgenic plants
have the ability to encapsidate even
unrelated infecting viruses (Refs. 94, 95,
96, and 97). However, heterologous
encapsidation involving a viral
transgene can only occur if an expressed
coat protein possesses the appropriate
physical parameters to encapsidate the
viral genome of infecting viruses. When
transgenic plants containing a PVCP-PIP
display resistance with very low or no
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levels of PVC-protein expression (e.g.,
due to PTGS), the probability of
heterologous encapsidation would be
very small or non-existent. (For a more
detailed discussion of PTGS and
suppression of gene silencing, see Unit
II.E. above and Unit IV.F. of the
companion document also appearing in
today’s Federal Register.)
Environmental concerns associated
with heterologous encapsidation when
PVC-protein is expressed appear to be
largely mitigated by several factors. One,
the heterologously encapsidated viral
genome may not be able to replicate in
the new host plant and could therefore
not actually infect it. In addition, if
replication is possible in the new plant,
the replicating viral genome encodes for
and thus would produce its own coat
protein rather than that which
heterologously encapsidated it. This
virus would not be transmitted by the
new vector that brought the
heterologously encapsidated genome to
the new host plant. The epidemiological
consequences of such heterologous
encapsidation would thus be limited.
Another consideration for some viruses
is that effective vector transmission may
depend on more than the coat protein
(Refs. 98 and 99), requiring regions of
the viral genome not included in PVCPPIPs as defined for this proposal, e.g.,
coat protein read-through domains or
helper factors. Thus, in such cases, the
coat protein that could potentially
heterologously encapsidate another viral
genome would not contain all the parts
necessary to lead to a change in vector
specificity. In addition, in large
monocultures of crop plants, a vector is
most likely to move from plant to plant
within the field and to transmit even a
heterologously encapsidated viral
genome to a plant that the virus is
already able to infect (Ref. 98). Finally,
as with recombination, as long as the
PVC-protein expressed in the transgenic
plant is from a virus that normally
infects the plant in the area where it is
planted, the outcome of any
heterologous encapsidation that may
occur is expected to be the same in
transgenic plants as in natural, mixed
infections.
In addition to these considerations,
EPA evaluated whether a virus that is
heterologously encapsidated and carried
to a new host plant might be exposed to
a vector that feeds on the new host plant
and perhaps other plants the virus
ordinarily could not access. EPA
considered whether this new vector
might in some cases be able to transmit
the virus even though the virus would
now be encapsidated in its own coat
protein, thereby expanding the virus’
vector range. A new vector could
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possibly transfer the virus to new host
plants, thus expanding the plant host
range as well (Ref. 57). EPA considers
expansion of host range through
heterologous encapsidation to be an
extremely unlikely outcome because
such an outcome depends on each event
in a series of rare events occurring.
Should the probability of occurrence of
any one event in this series be zero, the
adverse event of an expanded host range
would not occur. In addition to the
events enumerated above, additional
events must also occur. First, a virus
must be heterologously encapsidated, an
event that is possible only for some viral
genome-coat protein combinations.
Second, a new vector must transmit the
encapsidated viral genome. Third, the
transmission must be to a new host
plant. Fourth, the heterologously
encapsidated viral genome must be able
to replicate in the new host plant. Fifth,
the resulting virus, now encapsidated in
its own coat protein, must be exposed
to a new vector the virus never
encountered before that is nevertheless
able to transmit it. Finally, this vector
must transmit the virus to a new plant
that the virus’ prior vectors never
visited. For such a series of events to be
novel, the viruses, vectors, and plants
involved must have had no previous
opportunity to interact, and it is rare for
such a condition to be met. For
example, it is known that many viruses
are transmitted by polyphagous insects,
which would have already allowed the
viruses to be introduced to many
potential plant species even in the
absence of heterologous encapsidation
(Ref. 57). Moreover, viruses may be
transmitted at low frequency by a range
of species other than their primary
vector or mechanically, e.g., through the
practices of modern agriculture (Ref.
98).
Another scenario EPA considered is
one where a high enough frequency of
vector transmission to a new host plant
due to heterologous encapsidation
might mean that secondary spread
among new plant hosts might not be
required for the phenomenon to affect
the population, assuming that the virus
is able to decrease the new host plant’s
growth and/or reproduction. Although
this scenario may be more likely to
occur than an expansion of host range
given that fewer rare events would have
to occur, any impact on the affected
plant population would be highly
localized being confined to plants in or
near transgenic crop fields. Such
negative impacts are unlikely to be
sufficiently detrimental to require
FIFRA regulation given their localized
nature and the probability that common
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agricultural practices (e.g., vector
control) could be used to manage the
problem. Moreover, although isolated
instances of transmission may occur, a
significant proportion of a plant
population is unlikely to be infected in
such a scenario. For example, a field
experiment (discussed in Unit
III.D.1.iv.) showed that heterologous
encapsidation led to infection of only
2% of plants compared to 99% of plants
infected under similar conditions by a
virus that is not heterologously
encapsidated (Ref. 100). Most
importantly, the heterologously
encapsidated virus will still have no
way to spread among or beyond the
plants of the affected population. In the
case where a plant population contains
relatively few individuals such that the
impact of single plant infections would
be magnified, plant infections are even
less likely to occur because in addition
to the inefficient nature of heterologous
encapsidation, the vector would be
more likely to feed on the more
abundant transgenic crop plants. In
some cases a vector may have a strong
preference for a specific plant over even
closely related plants (Ref. 101).
Finally, EPA evaluated whether after
expansion to a new host, rapid selection
of variants best adapted to the new
environment might lead to the evolution
of a new virus (Ref. 57). However, in
addition to requiring several of the rare
events discussed above to occur, this
phenomenon is unlikely to be entirely
novel in any circumstance. All viruses
that are occasionally heterologously
encapsidated and transmitted to a new
plant host have had the opportunity to
adapt to new plant environments. The
opportunities for rapid viral evolution
presented by transgenic plants
containing PVCP-PIPs would not be
fundamentally different from what
occurs in nature under reasonably likely
circumstances. Rapid viral evolution
after heterologous encapsidation is not
dependent on the unique combination
of viruses that interact but rather the
introduction of a virus to a new plant
host, an event that likely occurs in
nature at some frequency for most
viruses either through heterologous
encapsidation or through occasional
transmission that occurs mechanically
or from secondary vectors (Ref. 98).
iii. Synergy. In synergy, another type
of viral interaction, the disease severity
of two viruses infecting together is
greater than expected based on the
additive severity of each virus alone.
For example, when a plant containing
potato virus X (PVX) is coinfected with
any of a number of potyviruses
including tobacco vein mottling virus,
tobacco etch virus, and pepper mottle
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virus, the disease symptoms are
considerably worsened and PVX
accumulates to a greater concentration
(Ref. 102). A listing of reported viral
synergisms has been compiled (Ref.
103).
In developing this proposal, EPA
addressed whether synergy could occur
between an infecting virus and a PVCPPIP, thereby increasing the severity of
the infecting virus and whether any
consequences for the environment could
result from such an increase. For disease
severity to worsen, the PVC-protein
must be at least one of the factors
causing synergy. However, the coat
protein is considered much less likely to
be responsible for synergism than other
parts of the virus (Refs. 104 and 105),
and a PVCP-PIP producing other viral
proteins would not qualify for this
proposed exemption. In addition, any
negative effects are expected to manifest
primarily in the transgenic crop itself.
Furthermore, any negative effects are
expected to be self-limiting because any
plants containing a PVCP-PIP that is
prone to display synergy with viruses
common in the areas of planting would
be quickly abandoned once such effects
were detected, perhaps as early as the
field-testing stage of product
development. Synergistic interactions
can be evaluated in transgenic plants
before deployment by experimental
inoculation with all of the viruses likely
to be encountered in the field (Ref. 98).
Developers have a strong incentive to
undertake such efforts to ensure the
efficacy of their product after
deployment.
iv. Field experiments. The
experiments referenced in Units III.E.2.i.
through iii. above investigated potential
viral interactions in transgenic plants
containing a PVCP-PIP under laboratory
conditions. However, equally important
is consideration of the likelihood and
potential impact of viral interactions
under natural field conditions (Ref.
106). Relatively few field studies have
been conducted to address the questions
EPA is evaluating for this proposal, but
the Agency has carefully considered the
available literature in developing this
proposed exemption.
A 6–year experiment searched for and
failed to find evidence of interactions
involving viral transgenes in 25,000
transgenic potato plants transformed
with various PLRV coat protein
constructs. Plants were exposed to
infection by PLRV by direct inoculation,
plant-to-plant spread, or natural
exposure. In field experiments, plants
were also naturally exposed to the
complex of viruses that occur in the
region. Both the greenhouse and field
tests failed to show any change in the
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type or severity of disease symptoms,
and all viruses isolated were previously
known to infect the plants and had the
expected transmission characteristics
(Ref. 107). These results suggest that
viral interactions leading to evolution of
new viruses and/or more severe viral
disease are events too rare to be detected
in a field trial of this size and duration.
A 2–year experiment with transgenic
melon and squash expressing coat
protein genes of an aphid-transmissible
strain of CMV failed to yield evidence
that either recombination or
heterologous encapsidation enabled
spread of an aphid non-transmissible
strain of CMV in the field (Ref. 108). A
similar experiment used transgenic
squash expressing coat protein genes of
an aphid-transmissible strain of
watermelon mosaic virus (WMV). Plants
were mechanically inoculated with an
aphid non-transmissible strain of
ZYMV, and subsequent transmissions of
the virus (assumed to be vectored by
aphids) were assessed. Infections of
ZYMV were not detected in
nontransgenic fields, but the virus
infected up to 2% of plants in
transgenic fields. Several lines of
evidence suggested ZYMV infection was
mediated by the WMV PVC-protein
heterologously encapsidating the ZYMV
viral genome. However, the virus spread
over short distances, and transmission
at a low rate failed to lead to an
epidemic of ZYMV in fields of WMVresistant transgenic squash despite the
presence of optimal conditions for
transmission (Ref. 100). These results
support the contention that even if
heterologous encapsidation involving a
PVC-protein were to occur, the impact
is likely to be negligible because each
plant infection by a heterologously
encapsidated virus requires a series of
rare events to occur. Viral infection by
normal routes of transmission can be at
least an order of magnitude more
efficient and lead to relatively greater
impacts (Ref. 100).
An experiment to assess the biological
and genetic diversity of California CMV
isolates sampled before and after
deployment of transgenic melon
containing the CMV coat protein gene
documented only one CMV isolate that
had significant sequence changes.
However, the same change was seen
with infection of non-transgenic plants,
suggesting that this isolate did not result
from recombination between the
transgene and an infecting virus (Ref.
109). The only field experiment to
directly assess the effect of
recombination in a transgenic plant
containing a PVCP-PIP found no
detectable grapevine fanleaf virus
(GFLV) recombinants containing the
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inserted coat protein sequence over the
course of a 4–year study (Ref. 110). Test
plants consisted of nontransgenic scions
grafted onto transgenic and
nontransgenic rootstocks that were
exposed over 3 years to GFLV infection
at two locations. Analysis of challenging
GFLV isolates revealed no difference in
the molecular variability among isolates
from 190 transgenic and 157
nontransgenic plants, or from plants
within (253 individuals) or outside (94
individuals) of the two test sites.
2. Proposed exemption criterion. The
information in Units III.E.2.ii. through
iv. suggests that heterologous
encapsidation very rarely leads to
changes in virus epidemiology that
could have any large-scale impact and
that synergy in plants containing PVCPPIPs is also unlikely to cause any
widespread environmental harm.
Consistent with these observations, the
2004 SAP noted that ‘‘except perhaps
for a very few cases, neither
heterologous encapsidation nor synergy
should be considered to be of serious
concern’’ (Ref. 60). However, the
Agency believes that in all cases,
concerns associated with these types of
viral interactions are likely to be limited
in scope (for reasons discussed in Units
III.E.2.ii. through iii.) such that the
determination can be made that they
pose low risk to human health and the
environment. EPA therefore concludes
that PVCP-PIPs present low risk with
respect to heterologous encapsidation
and synergy and that PVCP-PIPs could
be exempted without further
qualification or requirements to address
these endpoints.
However, EPA is not able to conclude
at this time that all PVCP-PIPs are low
risk with respect to recombination
(although see Unit VII for a discussion
of EPA’s request for information that
might allow the Agency to reach such a
conclusion). The Agency notes that the
vast majority of interactions between a
viral transgene and an infecting virus
are expected to be no different from
those that would occur in a natural
mixed infection of the respective viruses
and would not cause any adverse
environmental effects beyond what
could occur in the absence of the PVCPPIP. Nevertheless, the information
discussed in Unit III.D.1.i. suggests that
recombination among viruses may lead
to rare instances of adverse changes in
virus epidemiology and/or
pathogenicity, e.g., a host range
expansion. Based on the available
information, EPA is not able to rule out
that viable, recombinant viruses
containing a portion of a PVCP-PIP
could arise in transgenic plants and that
in a small set of circumstances
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(discussed in Unit III.D.2.i.) such
recombinants could be unlike those that
could arise naturally. EPA agrees with
the conclusions of the 2004 SAP that
‘‘[i]n contrast to heterologous
encapsidation and synergy, at least in
theory, the impact of recombination
could be much greater, since there is
now abundant bioinformatic evidence
that recombination has indeed, as long
suspected, played a key role in the
emergence of new viruses over
evolutionary time’’ (Ref. 25). The 2005
SAP concurred with this conclusion by
noting that there ‘‘are a few scenarios,
however, in which recombination may
have an incrementally higher
probability of creating a virus with new
properties. In conclusion, the Panel
recommended the need for the Agency
to have criteria to assess the level of
risk’’ (Ref. 11).
The Agency notes that the 2005 SAP
concluded that ‘‘the likelihood for
‘novel’ interactions is very low, and the
environmental concerns that might
result from using PVCP-PIPs in the
United States... is lower than that which
occurs naturally from mixed virus
infections’’ (Ref. 11). In addition, ‘‘it
was repeatedly stated that the
consequences of any recombination
event are minimal. This conclusion was
based on the fact that nearly every plant
on the planet is harboring multiple virus
infections with both closely related and
taxonomically distinct viruses, with
essentially no new viruses emerging
with substantially different properties
and causing wide pandemics or
undesirable environmental effects’’ (Ref.
11). In spite of such comments, EPA’s
proposal contains § 174.27(b) because of
the overall context of the Panel’s
response which articulated several
factors (discussed in Unit III.D.2.) that
should be considered when evaluating
recombination. EPA believes § 174.27(b)
is consistent with these comments of the
2005 SAP because the Agency believes
these comments apply only when
considering the whole set of PVCP-PIPs
that are likely to be developed. For the
PVCP-PIPs that would only qualify for
an exemption without the limitations
provided by § 174.27(b), EPA does not
believe the Agency can conclude low
risk with respect to recombination
because the 2004 and 2005 SAPs have
identified specific instances where this
general conclusion may not hold.
The few field evaluations conducted
(discussed in Unit III.D.1.iv.) suggest
that adverse environmental effects due
to recombination in transgenic plants
containing PVCP-PIPs are unlikely to
occur at least on a small scale over a
short time period. However, large
acreages of plants containing a PVCP-
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PIP grown over many years may provide
increased opportunity for rare events to
occur that are unlikely to be detected in
experimental studies (Ref. 104). In
addition, none of the experimental
systems described above would be
predicted to involve viruses that would
otherwise not be expected to interact in
a mixed infection found in nature.
Given the limited amount of field data
available, particularly data relevant to
the circumstances EPA has identified as
being of highest concern (i.e., those that
could lead to novel interactions), EPA is
limiting the proposed exemption to
those PVCP-PIPs for which novel viral
interactions are unlikely to occur. When
EPA consulted the 2004 SAP about
situations in which novel viral
interactions might be a concern, the
Panel agreed ‘‘that recombination is a
concern when the two contributing
viruses have not previously had a
chance to recombine’’ (Ref. 25).
In addition to considering the
potential for novel viral interactions to
occur, EPA also considered whether
transgenic plants containing PVCP-PIPs
might have a changed frequency of viral
interactions. The frequency could
decrease because the cellular
concentration of viral RNA transcripts
expressed from transgenes may be
orders of magnitude lower than the
concentration of viral RNA commonly
found in natural, mixed infections (Ref.
111), reducing the opportunity for
recombination. The concentration of
infecting viral RNA from the target virus
would also be reduced considerably if
the PVCP-PIP is efficacious, particularly
when the mechanism of resistance relies
on PTGS to remove viral RNA
transcripts with homology to the
transgene (Ref. 112), thereby also
reducing the opportunity for
recombination. However, the frequency
of interactions could also increase given
that transgene RNA expressed from a
constitutive promoter could be available
for interactions with infecting viruses in
all cells of the plant at all times - unlike
RNA from a virus in a natural infection.
When a virus invades a cell, it often
replicates and then moves to other cells
within the plant. The RNA remaining in
the initially infected cell becomes
encapsidated and may no longer be
available for interactions with another
invading virus (Ref. 113). When EPA
presented this issue to the 2004 SAP,
the panel responded that ‘‘no increase
in heterologous encapsidation should be
anticipated in PVCP-PIP plants’’ and
‘‘the Panel believed that in general
recombination was more likely to occur
in transgenic plants than in nonbioengineered plants.’’ Nevertheless, the
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Panel agreed ‘‘that the important
questions are not the relative likelihood
for recombination to occur, but rather
whether recombinants in transgenic
plants are different from those in nontransgenic plants and whether they are
viable’’ (Ref. 25). Thus, EPA’s proposal
focuses on situations in which novel
recombination events could occur due
to the presence of a PVCP-PIP.
i. Proposed categorical exemption
criterion in § 174.27(b)(1). In developing
the proposed categorical exemption for
a subset of PVCP-PIPs in which a
developer could self-determine whether
the criteria were met, EPA sought to
clearly identify those situations that
pose low risk with respect to viral
interactions.
A PVCP-PIP would meet the viral
interactions criterion under
§ 174.27(b)(1) if:
(i) The viral pathotype used to create the
PVCP-PIP has naturally infected plants in the
United States and naturally infects plants of
the same species as those containing the
PVCP-PIP, or
(ii) The genetic material that encodes the
pesticidal substance or leads to the
production of the pesticidal substance is
inserted only in an inverted repeat
orientation or lacking an initiation codon for
protein synthesis such that no PVC-protein is
produced in the plant.
Recombination between the coat
protein gene of the PVCP-PIP and
infecting viruses would be expected to
be of little concern in certain instances:
when such recombination would
involve segments of viruses that are
judged likely to have had the
opportunity to recombine in a natural,
mixed infection (and therefore any
recombinants produced are unlikely to
be novel), and when PTGS results in
only small, cleaved pieces of RNA being
available for recombination. The former
situation would be met if the conditions
of the criterion in proposed
§ 174.27(b)(1)(i) are met. The latter
situation would be met if the conditions
of the criterion in proposed
§ 174.27(b)(1)(ii) are met. EPA is
proposing that no further data or
information would be needed to
evaluate risks associated with
recombination when § 174.27(b)(1) is
satisfied under either § 174.27(b)(1)(i) or
§ 174.27(b)(1)(ii), and therefore no
Agency review would be necessary. The
developer may make this determination.
If the viral pathotype used to
construct the PVCP-PIP was isolated in
the United States from the same plant
species as was engineered to contain the
PVCP-PIP, the PVCP-PIP would meet
the proposed criterion in
§ 174.27(b)(1)(i). It should be noted that
this proposed criterion would be used
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in concert with the proposed protein
production criterion in § 174.27(c)
discussed below in Unit III.E.2., which
ensures that any modifications from the
natural isolate encode a protein that is
no more than minimally modified from
a natural virus coat protein. Thus, any
coat protein that satisfies § 174.27(c)
would be extremely unlikely to confer
significantly different properties on any
virus that could potentially acquire the
coat protein through recombination
with the genetic material of the PVCPPIP.
The Agency asked the FIFRA SAP
during the October 2004 meeting to
what extent PVCP-PIPs in plants might
present a potential concern should
interactions with infecting viruses
occur. The Panel expressed concern
only ‘‘about certain limited situations’’
and clarified that ‘‘in most cases there
is little a priori reason to believe that
recombinants between viruses and
transgenes will be more of a problem
than recombinants between two viruses
infecting the same plant, unless
transgenes are derived from severe or
exotic isolates. The general
recommendation to use mild, endemic
isolates as the source of the transgene
(e.g. Hammond et al. 1999) should
minimize any potential for creation of
novel isolates that would not equally
easily arise in natural mixed infections’’
(Refs. 25 and 57). The Agency’s
proposed § 174.27(b)(1)(i) is consistent
with this 2004 SAP recommendation
because it excludes exotic virus isolates
as the source of the PVCP-PIP transgene.
Although proposed § 174.27(b)(1)(i)
does not require that the virus isolate be
a ‘‘mild’’ form of the virus, it does
ensure that when virus isolates capable
of causing severe cases of viral disease
are used, the PVCP-PIP may only meet
§ 174.27(b)(1)(i) if the viral pathotype
was present in the natural system and
therefore should pose no risk of novel
interactions.
The 2005 SAP offered a decision
flowchart indicating a point at which
the Agency should identify the few
scenarios where recombination may be
of concern: ‘‘the question arises as to
whether recombination of the sequence
could lead to a significant change in the
properties of the recombinant over the
original properties of the superinfecting
virus. Significant changes include
increase in pathogenicity, increase of
host range or change of vector’’ (Ref. 11).
EPA believes that consideration of
whether the conditions of proposed
§ 174.27(b)(1)(i) are met addresses
whether the potential exists for
significant changes in the properties of
a recombinant virus compared to what
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might occur in a natural, mixed
infection.
In addition to excluding exotic virus
isolates, proposed § 174.27(b)(1)(i) also
excludes PVCP-PIPs that are inserted
into a plant species that is not naturally
infected by the virus used to create the
PVCP-PIP. Most PVCP-PIPs are created
from viruses that do naturally infect the
plant species into which they are
inserted because greater efficacy is
achieved when a virus most similar to
the target virus is used as the source of
the sequence used in the PVCP-PIP.
However, virus-resistant transgenic
plants have been created where this is
not the case (Ref. 114). In these
situations, a virus is introduced into a
system where it does not naturally
occur, and viruses with which it does
not otherwise interact may be present in
that system. The Agency cannot a priori
determine that such interactions are safe
because there is no experience upon
which to base such a finding.
Proposed § 174.27(b)(1)(i) is also
consistent with the 2005 SAP’s
recommendation to consider ‘‘whether
recombination of the sequence could
lead to a significant change in the
properties of the recombinant over the
original properties of the superinfecting
virus’’ (Ref. 11). When the viral
pathotype used to create the PVCP-PIP
has naturally infected plants in the
United States and naturally infects
plants of the same species as those
containing the PVCP-PIP, the sequences
that could interact would be expected to
already have opportunities to interact in
nature and thus no novel recombinants
should be produced.
The Agency’s proposed
§ 174.27(b)(1)(ii) is consistent with the
2005 SAP’s recommendation to consider
whether the PVCP-PIP expresses PVCprotein when evaluating the potential
consequences of recombination (Ref.
11). When a PVCP-PIP expresses no
PVC-protein because it is designed to
mediate resistance through PTGS,
recombination would be of little
concern because ‘‘recombination
between a full-length viral RNA and a
cleaved small RNA resulting from PTGS
would yield a truncated non-functional
RNA. Therefore, a PTGS transgene poses
negligible potential to yield novel
recombinant viruses’’ (Ref. 11). EPA
therefore makes part of its proposal two
circumstances when, according to the
2005 SAP, the PVCP-PIP can only
mediate resistance through PTGS
because it would produce no PVCprotein: when the genetic material that
encodes the pesticidal substance or
leads to the production of the pesticidal
substance is inserted only in an inverted
repeat orientation or lacking an
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initiation codon for protein synthesis
such that no PVC-protein is produced in
the plant (Ref. 11). See Unit III.D.2.ii.
below for a discussion of how other
constructs mediating resistance through
PTGS could meet § 174.27(b).
One Panel member noted, ‘‘PTGS
results in small RNA from the PIP and
the infecting virus that could, in certain
circumstances, be recombinatorial.’’
However, the Panel concluded ‘‘this
minimal RNA would not confer a
phenotype to the recombinant, would
result in just a few nucleotide changes
in a potential recombinant, and thus
would be irrelevant’’ (Ref. 11).
EPA proposes to define the term
‘‘naturally infect’’ to mean ‘‘to infect by
transmission to a plant through direct
plant-to-plant contact (e.g., pollen or
seed), an inanimate object (e.g., farm
machinery), or vector (e.g., arthropod,
nematode, or fungus). It does not
include infection by transmission that
occurs only through intentional human
intervention, e.g., manual infection in a
laboratory or greenhouse setting.’’ The
Agency is proposing this definition
specifically to exclude transmission that
occurs only through intentional human
intervention because such transmission
would have little relevance to normal
virus infection. EPA recognizes that
humans may play an inadvertent role in
infection (e.g., by transmitting the virus
on farm machinery). Such unintentional
(and often unavoidable) transmission
can be an important means of virus
transmission, leading to the natural
presence of viruses in plants. EPA
therefore proposes to include this mode
of incidental transmission in the
definition of naturally infect.
EPA uses the term ‘‘viral pathotype’’
rather than the more generic term
‘‘virus’’ in response to the October 2004
FIFRA SAP comment that ‘‘[n]ot all
isolates of a virus infect and cause
disease in all plant genotypes and, as a
consequence, the unqualified use of the
term ‘virus’ when setting a condition for
applicants to the Agency [is] not
adequate in this context. It is therefore
appropriate in the context of biosafety
as well as virus epidemiology to
recognize the value of defining specific
viral pathotypes or host range variants.’’
The 2005 SAP was asked to comment on
the use of this term and responded,
‘‘there was not much discussion of this
term. The Panel suggested that logic
says that local or indigenous virus
isolates, or those with significant
sequence similarity, will be used to
generate PVCP-PIPs. From what we
know now, only those viruses with high
sequence identity will be useful as
sources of the PVCP-PIP transgene.’’
EPA agrees that generally viral
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pathotypes that meet § 174.27(b)(1) will
be those most effective for creating
PVCP-PIPs and will therefore be the
most commonly used. However, EPA
considers the limitations imposed by
this term to be necessary because the
Agency cannot conclude that viruses
not meeting this criterion would be low
risk with respect to recombination.
In this proposed criterion and in
§ 174.27(c) discussed below, EPA uses
the phrase ‘‘genetic material that
encodes the pesticidal substance or
leads to the production of the pesticidal
substance,’’ rather than the phrase
‘‘genetic material necessary for the
production,’’ to indicate that regulatory
regions, such as promoters, enhancers,
or terminators, need not be considered
in evaluating whether a PVCP-PIP
satisfies these criteria. EPA is not
proposing to amend the definitions for
‘‘genetic material necessary for the
production’’ or ‘‘regulatory region,’’
both found at 40 CFR 174.3, and is not
seeking any comment on these
definitions.
ii. Proposed exemption criterion
conditional on Agency determination in
§ 174.27(b)(2). The Agency recognizes
that many PVCP-PIPs may pose low risk
with respect to recombination even
though they fail to satisfy § 174.27(b)(1).
Therefore, EPA is proposing an
approach under which PVCP-PIPs that
fail to meet § 174.27(b)(1) could still
meet § 174.27(b), subject to an Agency
review to determine whether they meet
a different set of conditions related to
this issue. Under this proposed
approach, a PVCP-PIP would meet
§ 174.27(b) under § 174.27(b)(2) if the
Agency determines that viruses that
naturally infect the plant containing the
PVCP-PIP are unlikely to acquire the
coat protein sequence through
recombination and produce a viable
virus with significantly different
properties than either parent virus.
The conditions in proposed
§ 174.27(b)(1) address the potential for
recombinants to arise unlike those
expected in natural mixed infections
primarily by ensuring that no novel
viral interactions occur. Under proposed
§ 174.27(b)(2), a PVCP-PIP could qualify
for exemption even when novel viral
interactions could occur providing steps
were taken to ensure that an infecting
virus would not acquire a portion of the
PVCP-PIP coat protein sequence through
recombination and produce a viable
virus with significantly different
properties than either parent virus.
Experimental evidence has suggested
a number of ways coat protein genes of
certain viruses may be modified in
constructing a PVCP-PIP to reduce the
possibility they would participate in a
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recombination event with an infecting
virus. For example, removing the 3′
untranslated region (UTR) in the coat
protein mRNA transcript may be
effective at reducing recombination for
viruses that carry the initiation
promoters of RNA replication in this
region (Ref. 115). Evidence suggests that
recombination among RNA viruses
occurs via template switching by the
viral replicase during replication such
that a hybrid molecule is formed (Ref.
116). Inclusion of the 3′ UTR may
enable replication to begin on the
mRNA transcript and then switch to the
RNA of the invading virus. Removal of
this region would necessitate two
separate template-switching events to
form a successful recombinant and thus
reduce its likelihood of occurrence (Ref.
80). Experiments with CCMV
demonstrated that deletions in the 3′
UTR did indeed reduce the recovery of
recombinant viruses (Ref. 117). Since
functional resistance is still conferred
by constructs containing a CP lacking
the 3′ UTR, this region may not be
necessary. Other techniques that have
been suggested include:
• Reducing the extent of shared
sequence similarity between the
infecting virus and the transgene to
reduce the opportunities for
homologous recombination (Ref. 118).
• Excluding any sequences
containing replicase recognition sites
that are potential sites of recombination
and any sequences known or thought to
be recombination hotspots, e.g.,
promoters for genomic and subgenomic
RNA synthesis (Ref. 119).
• Avoiding potential hairpin
structures in the transgene that might
function as acceptor structures for the
replicase complex (Ref. 120).
It is important to note that any PVCprotein produced must be evaluated
under § 174.27(c) in order for the PVCPPIP to qualify for exemption. Some
techniques that may enable a PVCP-PIP
to meet § 174.27(b)(2) would preclude
the PVCP-PIP from meeting
§ 174.27(c)(1) and necessitate a review
under § 174.27(c)(2). For example, a
construct could meet proposed
§ 174.27(b)(2) if it contained portions of
several different coat protein genes in
tandem, linked together in such a way
that if the sequence were translated it
would yield a non-functional coat
protein of no use to a virus. A virus that
acquired this entire sequence through
recombination in exchange for portions
of its own genome would likely be
nonviable. As another example, a
construct might meet proposed
§ 174.27(b)(2) if it contained a very
small portion of a coat protein gene. In
such cases, a virus would be unlikely to
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acquire this sequence through
recombination without picking up
additional pieces of genetic material
from the construct or the plant genome
that would likely render the virus
nonviable. Or, if a virus did acquire a
piece of just the small part of the coat
protein sequence contained in the
transgenic plant, it would likely not be
large enough to significantly change the
properties of the parent virus. Any PVCprotein produced from either such
construct would fail to meet
§ 174.27(c)(1) but could be evaluated
under and may nevertheless meet
§ 174.27(c)(2) (see Unit III.E.2. below).
EPA recognizes the comments of the
2004 SAP that ‘‘methods for minimizing
recombination are only partially
effective. For this reason, the question
remains whether novel recombinants
would be created in transgenic plants,
and simply reducing the frequency of
these events is not an answer to the
question’’ (Ref. 60). However, EPA
believes that a combination of two or
more methods, or even perhaps a single
method in some cases, could be
employed to reduce the expected
frequency of recombination such that
the Agency would be able to make a
determination that a PVCP-PIP would
pose low risk with respect to viral
interactions. EPA asked the 2004 SAP
‘‘which methods are sufficiently
effective such that requiring
measurement of recombination rates
would be unnecessary. The Panel
doubted if the... methods [discussed] are
sufficiently effective to warrant the
reduction of recombination rates below
the level that the actual measurement
will be unnecessary’’ (Ref. 25).
However, the Agency would have the
opportunity during the case-by-case
Agency review under § 174.27(b)(2) to
consider the particular viral system and
whether literature supports the
contention that the recombination
reduction techniques are likely to be
sufficiently effective in the system in
which they are employed. EPA
anticipates that the Agency could base
this determination on the expected
reduction in frequency of recombination
as determined from the literature and
that actual measurement of
recombination rates may be
unnecessary. Given that there is no
universally applicable method for
reducing recombination frequency and
this type of case-by-case consideration
of the particular virus system in
question must be conducted, EPA
believes an Agency review is needed to
make this determination. With an
Agency determination under
§ 174.27(b)(2), EPA would create a
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criterion that would encompass a larger
set of those PVCP-PIPs that pose low
risk with respect to viral interactions
than are covered under § 174.27(b)(1).
Section 174.27(b)(2) is consistent with
the advice of the 2005 SAP in that it
incorporates the portions of the
proposed decision tree that allow
consideration of whether there are
‘‘features controlling recombination,’’
whether ‘‘the protein [is] complete,’’
and whether the plant host contains
‘‘genes that reduce recombination’’ (Ref.
11). Likewise, the review procedures for
determining whether a PVCP-PIP met
the conditions of § 174.27(b)(2) would
also be able to consider ‘‘the type of
RNA-dependent RNA polymerase
(RdRps) encoded by the superinfecting
virus and the compartmentalization of
its site of replication’’ as suggested by
the 2005 SAP (Ref. 11). Although EPA
notes that there was some disagreement
among the Panel members about the
appropriateness of including such
information as part of the flow chart, the
Agency believes that this information
could be reasonably considered when
available and when sufficient
knowledge about the plant/virus system
exists such that it would offer useful
information for evaluating this criterion.
Overall, § 174.27(b) thus enables the
Agency to consider either under
§ 174.27(b)(1) or § 174.27(b)(2) all of the
factors mentioned in the flowchart by
the 2005 SAP.
3. Historical approaches still under
consideration. EPA’s proposed
exemption in 1994 did not contain any
criteria related to viral interactions.
However, since that time, many
additional scientific papers and reviews
have been published on this topic. Most
affirm the general safety of PVCP-PIPs
with respect to viral interactions, but
some call into question assumptions of
how generically this conclusion holds
across all PVCP-PIPs. For example,
although the 2000 NRC report stated
that ‘‘[m]ost virus-derived resistance
genes are unlikely to present unusual or
unmanageable problems that differ from
those associated with traditional
breeding for virus resistance,’’ the NRC’s
report also suggested that their
conclusions were based on the
assumption that certain risk
management strategies should or would
be implemented, e.g., elimination of
specific sequences to limit the potential
for recombination (Ref. 10). EPA
believes the Agency’s 1994 conclusion
of low probability of risk still holds for
most PVCP-PIPs. However, in order to
grant an exemption under FIFRA, EPA
must be able to make such a finding for
all PVCP-PIPs covered by the exemption
and must make its safety determination
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in the absence of any regulatory
oversight under FIFRA that could
ensure mitigation measures, such as
those discussed in the NRC report, were
employed. Therefore, it appears prudent
at this time to limit this proposed
exemption with a criterion that restricts
the potential for novel recombination
events, as these have been identified as
the rare situation in which viral
interactions in plants containing a
PVCP-PIP may lead to adverse
environmental effects.
EPA presented a set of conditions to
the 2004 SAP and asked whether they
would significantly reduce either the
novelty or frequency of viral
interactions in plants containing PVCPPIPs such that the Agency would not
need to regulate the PVCP-PIP (Ref. 25).
The first proposed condition was that
‘‘the genetic material of the PVCP-PIP is
translated and/or transcribed in the
same cells, tissues, and developmental
stages naturally infected by every virus
from which any segment of a coat
protein gene used in the PVCP-PIP was
derived.’’ EPA considered such a
condition because with a PVCP-PIP,
plants may express viral genes in cells
and/or tissues that the virus does not
normally infect. Genetic promoters
currently used in most transgenic plants
cause constitutive expression of
transgenes at developmental stages that
might otherwise be unaffected by viral
infection and often in tissues that the
virus does not normally infect (Ref.
113). For example, luteoviruses are
normally expressed only in phloem
tissue, but the cauliflower mosaic virus
(CaMV) promoter, commonly found in
existing PIP constructs, would drive
expression of luteoviral coat protein in
all plant cells. Some evidence suggests
that in natural infections different
viruses have different temporal or
spatial expression patterns that would
limit their interactions (Refs. 63, 121,
and 122). However, the 2004 SAP
concluded that such a condition would
be of limited utility because ‘‘[m]ost
plant viruses are present in a wide range
of cell and tissue types’’ (Ref. 25).
The second condition proposed to the
2004 SAP was that ‘‘the genetic material
of the PVCP-PIP contains coat protein
genes or segments of coat protein genes
from viruses established throughout the
regions where the crop is planted in the
United States and that naturally infect
the crop into which the genes have been
inserted.’’ EPA considered the first part
of this criterion because plants may be
engineered with coat protein genes from
an exotic strain of a virus that may be
more virulent or have other properties
different from endemic isolates.
Interactions between a PVCP-PIP based
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on such virus sequences and infecting
viruses could potentially change the
epidemiology or pathogenicity of the
infecting viruses. The 2004 SAP
concurred that ‘‘using such an exotic
coat protein gene would open
possibilities for novel interactions.’’
EPA’s current proposed § 174.27(b) thus
excludes from exemption PVCP-PIPs
based on coat protein genes from exotic
viruses unless steps have been taken to
reduce the frequency of recombination.
EPA considered the second part of
this 2004 criterion (i.e., the genetic
material of the PVCP-PIP contains coat
protein genes or segments of coat
protein genes from viruses... that
naturally infect the crop into which the
genes have been inserted) because in
heterologous resistance a plant may be
resistant to infection by a particular
virus in spite of having the coat protein
gene of another virus incorporated into
its genome. For example, coat protein
genes from LMV were used to provide
resistance to PVY in tobacco which is
not infected by LMV (Ref. 114). In such
plants, LMV sequences might have a
new opportunity to interact with viruses
that infect tobacco. The 2004 Panel
concluded that ‘‘[w]hat is described
here is most often implemented: in
designing a PVCP transgene, better
efficacy is often observed if it is as
similar as possible to the target virus.’’
Nevertheless, EPA believes that EPA’s
current proposed criterion (b) is
appropriate given that PVCP-PIPs may
be developed using heterologous
resistance. This criterion excludes from
exemption PVCP-PIPs used in plants
that the virus used to create the PVCPPIP does not naturally infect unless
steps have been taken to reduce the
frequency of recombination.
The third condition proposed to the
2004 SAP was that ‘‘the PVCP-PIP has
been modified by a method
scientifically documented to minimize
recombination (e.g., deletion of the 3′
untranslated region of the coat protein
gene). As discussed above, the 2004
SAP expressed reservation about such a
criterion, and EPA recognizes that any
single method for minimizing
recombination may be only partially
effective (Ref. 60). However, EPA
believes that a combination of two or
more methods, or even perhaps a single
method in some cases, could be
employed such that the expected
frequency of recombination would be
reduced to a level that would support
determination that a PVCP-PIP would
pose low risk with respect to viral
interactions, but that such a
determination could only be made on a
case-by-case basis. EPA thus intends
that the proposed criterion in
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§ 174.27(b)(2)(ii) would allow the
Agency to make this determination after
review.
The fourth condition proposed to the
2004 SAP was that ‘‘the PVCP-PIP has
been modified by a method
scientifically documented to minimize
heterologous encapsidation or vector
transmission, or there is minimal
potential for heterologous encapsidation
because no protein from the introduced
PVCP-PIP is produced in the transgenic
plant or the virus does not participate in
heterologous encapsidation in nature.’’
The 2004 SAP concluded that ‘‘[t]his
method can... be considered seriously if
deemed necessary’’ (Ref. 25). However,
the Agency concluded (as discussed
above in Unit III.D.1.ii.) that such
methods are not necessary because
heterologous encapsidation is so rarely
likely to be of any significant ecological
concern.
Based on these considerations, EPA
presented a set of modified conditions
to the 2005 SAP that reflected the
advice of the 2004 SAP. Those
conditions were the same as those that
EPA is proposing today in § 174.27(b)
except that § 174.27(b)(2) as submitted
to the 2005 SAP included an additional
provision: this criterion could be met by
meeting the current conditions or by
meeting the condition that ‘‘the
properties of the viral pathotype that are
determined by the coat protein gene
used to create the PVCP-PIP are
substantially similar to the properties of
a viral pathotype that naturally infects
plants in the United States, and the viral
pathotype used to create the PVCP-PIP
naturally infects plants of the same
species as that containing the PVCPPIP.’’ EPA is no longer proposing this
condition as a means of meeting
§ 174.27(b) because the 2005 SAP
concluded that it was ‘‘unusable and
cannot be re-written into a satisfactory
form’’ because of the difficulty of
defining ‘‘properties’’ and ‘‘substantially
similar’’ in this context (Ref. 11).
E. Production of Proteins
1. Scientific issues. In addition to
weediness and viral interactions, a third
concern associated with PVCP-PIPs
relates to the potential production of
proteins (called PVC-proteins) from the
plant virus coat protein sequences of the
PVCP-PIP, i.e., the potential for human
or nontarget organism exposure to
proteins that have not previously
existed in nature and thus should be
examined to determine whether they
have potentially toxic or allergenic
properties. EPA must consider the safety
of any potentially expressed proteins
that are part of the PIP when proposing
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criteria to evaluate PVCP-PIPs for
possible exemption.
EPA considered human dietary,
human occupational, and nontarget
exposure risks in evaluating the safety
of PVC-proteins for purposes of this
proposal as the Agency must do when
evaluating whether a pesticide can be
exempt from the requirements of FIFRA.
See EPA’s assessment of human dietary
exposure risks and other nonoccupational exposure risks published
in the companion document in today’s
Federal Register that proposes to
establish a tolerance exemption under
FFDCA section 408 for residues of the
PVC-protein portion of a PVCP-PIP.
Many, if not all, of the considerations
used to evaluate the potential for novel
occupational or nontarget exposures can
be directly extrapolated from the
discussion in this companion document
describing EPA’s base of experience
with viruses infecting food plants. That
analysis led the Agency to draw three
conclusions on which it is relying to
support the proposed tolerance
exemption for residues of PVC-proteins
in food and which can also be used to
support this proposed criterion for
exemption from FIFRA requirements.
First, virus-infected plants have always
been a part of the human and domestic
animal food supply. Most crops are
frequently infected with plant viruses,
and food from these crops has been and
is being consumed without adverse
human or animal health effects. Second,
plant viruses are not infectious to
humans, including children and infants,
or to other mammals. Third, plant virus
coat proteins, while widespread in food,
have not been associated with toxic or
allergenic effects to animals or humans.
EPA derived these conclusions from a
sufficient experience and information
base to support the proposed tolerance
exemption and this proposed criterion
for exemption from FIFRA
requirements.
EPA consulted the 2004 SAP about
possible nontarget effects of PVCproteins and the validity of the Agency’s
risk assessment being based on the
known history of safe exposure to coat
proteins of naturally occurring plant
viruses. Virus infected plants have
always been a part of the natural
environment, and organisms that
interact with plants have likely been
exposed to plant virus coat proteins
over long periods of time. The panel
confirmed that PVC-proteins within the
range of natural variation of the virus
would not be anticipated to present
risks to nontarget organisms, concluding
that, ‘‘[l]ethal effects in animal life after
feeding on PVCP-PIP plants are highly
unlikely because plant viruses are not
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known to have deleterious effects on
animal life. Additionally, animals
routinely feed on non-engineered virusinfected plants and do not die....
[S]ublethal effects are not expected to be
manifested in animal life, again because
wildlife and insects regularly feed on
non-engineered virus-infected plants
with no apparent sublethal damage’’
(Ref. 60).
The 2005 SAP echoed these general
conclusions by pointing out that virus
coat proteins ‘‘are naturally present in
the environment and no adverse effects
to humans or non-targets have been
reported’’ (Ref. 11). However, the 2005
SAP also suggested that additional
concerns might warrant evaluation,
including ‘‘indirect ecological effects
(such as altered food sources, vegetative
cover, or microbial communities)’’ (Ref.
11). The particular concerns associated
with such effects were not articulated.
PVC-proteins that meet the conditions
of this exemption are not expected to
alter nontarget food sources because
they would be so similar to plant virus
coat proteins that occur naturally.
Indirect effects such as changes in
vegetative cover might occur if crop
plants containing a PVCP-PIP are larger
and/or more productive in the absence
of virus infection relative to plants that
are infected. However, the overall effect
on nontarget organisms is still likely to
be minor given that crops are often
grown in the absence of viral disease
even without the use of a PVCP-PIP, and
PVCP-PIPs exempted by this proposal
would have very limited ability to
spread from crop plants to wild or
weedy relatives. PVCP-PIPs are not
expected to impact microbial
communities because natural plant
virus coat proteins are not known to
have any toxic mode of action.
Moreover, plant virus coat proteins
already occur naturally in the
environment so microbial communities
are already exposed to such proteins.
Some Panel members also ‘‘expressed
concern over potential effects on
pollinators,’’ but EPA is unaware of any
scientific evidence supporting this
concern. EPA concurs with other Panel
members who believed that ‘‘a history of
exposure by pollinators to naturally
infected plants can be taken as
indicating that there are no novel risks’’
(Ref. 11).
Other concerns raised by the 2005
SAP regarding nontarget and human
non-dietary exposure are addressed in
the companion document published in
today’s Federal Register, where they are
discussed in the context of
consideration of the human dietary risks
associated with PVC-proteins. The
companion document describes in Unit
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IV.C., for example, the basis for EPA’s
conclusion that the hazard associated
with PVC-proteins that meet § 174.27(c)
of this proposed exemption is
sufficiently low that they do not rise to
the level warranting regulation. These
same arguments can be applied to PVCproteins that meet § 174.27(c) in this
proposal, even in the rare cases when
nontarget exposure to a PVC-protein
might be greater than the exposure to
the corresponding natural plant virus
coat protein. The companion document
also describes in Unit IV.C. rationales
that can be used to support EPA’s
conclusion that nontarget exposure to
PVC-proteins in plant tissues that do not
normally contain the corresponding
plant virus coat protein is unlikely to
contribute significantly to risk.
Nontarget organisms would be exposed
to natural plant virus coat proteins
through a variety of routes and there is
no evidence that they would be toxic to
any nontarget organisms regardless of
the route of exposure.
2. Proposed exemption criterion. As
with the other proposed criteria
discussed in this document, EPA is
proposing that § 174.27(c) would have
two parts: Section 174.27(c)(1) under
which a developer may self-determine if
a PVCP-PIP meets the conditions, and
§ 174.27(c)(2) under which the Agency
must make the determination.
i. Proposed categorical exemption
criterion in § 174.27(c)(1). In developing
the proposed categorical exemption for
a subset of PVCP-PIPs in which a
developer could self-determine whether
the criteria were met, EPA sought to
identify clearly those situations that
pose low risk with respect to protein
production because any PVC-proteins
produced would be within the range of
natural variation. EPA wants to ensure
that a long history of safe human and
nontarget exposure has occurred for any
PVC-protein produced from a PVCP-PIP
that could qualify for this exemption. A
PVCP-PIP would meet § 174.27(c)(1) if a
product developer self-determines that:
The genetic material that encodes the
pesticidal substance or leads to the
production of the pesticidal substance:
(i) Is inserted only in an inverted repeat
orientation or lacking an initiation codon for
protein synthesis such that no PVC-protein is
produced in the plant, or
(ii) Encodes only a single virtually
unmodified viral coat protein. Multiple PVCproteins could each separately meet this
criterion. Chimeric PVC-proteins do not
qualify.
EPA intends with the phrase ‘‘is
inserted only in an inverted repeat
orientation or lacking an initiation
codon for protein synthesis such that no
PVC-protein is produced in the plant’’
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to include only those PVCP-PIPs with
the specified types of constructs that the
2005 SAP indicated provide a high
degree of certainty that no PVC-protein
would be produced. Although other
types of constructs may also usually not
produce any PVC-protein, EPA believes
it is necessary to incorporate into its
proposal a provision for an Agency
review of such constructs. In such a
review, EPA could evaluate the level of
protein production, if any, that could
occur under a variety of circumstances
and environmental conditions
representative of those that the plant
may experience (see Unit III.E.2.ii.).
EPA includes the word ‘‘only’’ and the
phrase ‘‘such that no PVC-protein is
produced in the plant’’ in
§ 174.27(c)(1)(i) to ensure that the
proposed exemption encompasses only
those PVCP-PIPs that the 2005 SAP
indicated ‘‘could be safely determined
to have no [PVC-protein] expression
regardless of plant tissue,
developmental stage, environmental
conditions, or exposure to virallyencoded suppressors of PTGS’’ (Ref. 11).
The proposed exemption criterion in
§ 174.27(c)(1)(i) would not be met by a
PVCP-PIP when there are multiple-copy
insertions in the plant if any of the
copies is not in an inverted repeat
orientation or lacking an initiation
codon for protein synthesis.
The Agency proposes to define the
term ‘‘unmodified’’ to mean, ‘‘having or
coding for an amino acid sequence that
is identical to an entire coat protein of
a naturally occurring plant virus. The
Agency proposes to define the term
‘‘virtually unmodified’’ to mean,
‘‘having or coding for an amino acid
sequence that is identical to an entire
coat protein of a naturally occurring
plant virus, except for the addition of
one or two amino acids at the N- and/
or C-terminus other than cysteine,
asparagine, serine, and threonine and/or
the deletion of one or two amino acids
at the N- and/or C-terminus.’’ EPA’s
rationale for these proposed definitions
and alternative proposals for defining
‘‘virtually unmodified’’ are found in the
companion document published in
today’s Federal Register. The alternative
proposals for virtually unmodified will
also be considered as alternatives under
this FIFRA proposal.
EPA is proposing to exclude more
significantly modified PVC-proteins
from the proposed categorical
exemption by requiring that the genetic
material encode ‘‘only a single virtually
unmodified viral coat protein.’’ For
example, PVC-proteins containing
internal insertions, deletions, or amino
acid substitutions would be excluded,
as would be chimeric proteins that are
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encoded by a sequence constructed from
portions of two or more different plant
virus coat protein genes. EPA is
proposing to exclude such PVC-proteins
from the self-determining part of the
exemption in response to the advice of
the FIFRA SAP in October 2004 that,
‘‘[t]here was general agreement that an
allergenicity assessment2 would be
appropriate for insertions or deletions,
except perhaps for terminal deletions
that do not affect overall protein
structure.’’ Insufficient information
exists at this time to allow EPA to
describe a priori a criterion that would
ensure all PVC-proteins with
modifications other than those
encompassed by the definition of
‘‘virtually unmodified’’ fall within the
base of experience supporting the
proposed exemption. At this time, it is
not possible to make a categorical risk
assessment finding that other types of
changes are unlikely to change the
characteristics of any protein produced.
Thus, EPA proposes no other
modifications be allowed in PVCproteins that would meet § 174.27(c)(1).
EPA intends that multiple PVCproteins expressed in the same plant
could each separately meet the criterion
in § 174.27(c)(1)(ii) but that chimeric
PVC-proteins could not meet this
criterion. Chimeric proteins would
include PVC-proteins composed of the
fusion of two (or more) whole or partial
capsid proteins, as well as chimeric
proteins that contain a PVC-protein
fused with another, unrelated protein.
The 2005 SAP concluded that such
chimeric proteins could possibly have
‘‘completely different antigenic and
possibly allergenic properties compared
to the properties of the individual
capsid proteins’’ (Ref. 11). EPA is
therefore unable to conclude that such
proteins would be low risk without a
case-by-case review of the protein. EPA
intends that multiple, distinct PVCproteins produced, for example, from a
single transgene insertion event or from
multiple insertion events in the same
plant, could qualify for this exemption
because the Agency believes that the
properties of each individual protein
would be the relevant factors to
consider. Some members of the 2005
SAP believed that ‘‘EPA evaluations
should consider effects of multiple
constructs of PVCP-PIPs introduced in
transgenic plants’’ (Ref. 11). The
rationale for this concern appears based
in part on the potential for a synergistic
effect from multiple toxins. However,
PVC-proteins produced from a PVCP2 The concern relating to the need for an
allergenicity assessment is relevant to the Agency’s
determinations concerning occupational exposures.
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19621
PIP that could qualify for this
exemption would not be expected to
have any toxic mode of action that
could cause such a phenomenon. The
rationale for this concern appears to be
also based in part on the potential for
multiple PVC-proteins to ‘‘alter ‘natural’
protein production in plants’’ (Ref. 11).
However, EPA concurs with other 2005
SAP members who ‘‘believed that this
situation was no different than is likely
to occur in nature, where a plant might
be infected by multiple unrelated
viruses’’ (Ref. 11). (See also Unit IV.E.1.
in the companion document published
in today’s Federal Register for the basis
for EPA’s conclusion that exposure to
plants with different levels of proteins
elicited by pathogen attack, wounding,
or stress, i.e., ‘‘pathogenesis-related
proteins,’’ likely occurs normally.)
EPA believes the phrase ‘‘an entire
coat protein’’ in the definition of
‘‘virtually unmodified’’ conveys that
segments of PVC-proteins do not meet
the criterion in § 174.27(c)(1)(ii). This
limitation is based on the advice of the
2005 SAP that ‘‘[d]etermining whether
PVC-proteins containing terminal
deletions, or any other modifications,
are within the range of natural variation
would require the development of a
database of the natural variation and
truncated forms of PVC-proteins that
occur naturally.’’ As such, EPA could
more appropriately take this
consideration into account under the
criterion in § 174.27(c)(2)(i) which
contains provisions for an Agency
review (discussed below in Unit
III.E.2.ii.). However, EPA is considering
several alternative definitions for
‘‘virtually unmodified,’’ some of which
may allow truncated PVC-proteins to
meet the proposed criterion in
§ 174.27(c)(1)(ii). These alternatives are
presented and discussed in Unit IV.E.1.
of the companion document published
elsewhere in today’s Federal Register.
If the genetic material that encodes
the pesticidal substance or leads to the
production of the pesticidal substance
encodes only a single virtually
unmodified viral coat protein, no novel
exposures to humans or nontarget
organisms are likely to occur because
these PVC-proteins are essentially
identical to plant viral coat proteins that
are widespread in the plant kingdom, as
most plants are susceptible to infection
by one or more viruses. EPA is relying
on this history of safe exposure to
support this proposal. The Agency
believes that when such a PVCP-PIP is
used, the PVCP-PIP would pose low
probability of risk with respect to
protein production. EPA is proposing
that no further data or information
would be needed to evaluate this issue
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when § 174.27(c)(1) is satisfied, and
therefore no Agency review would be
necessary.
ii. Proposed exemption criterion
conditional on Agency determination in
§ 174.27(c)(2). The Agency
acknowledges that many PVCP-PIPs
may pose low risk with respect to
concerns associated with protein
production even though they fail to
satisfy § 174.27(c)(1). EPA is proposing
to review such PVCP-PIPs under slightly
different factors that the Agency
believes also ensure that qualifying
PVCP-PIPs pose low risk with respect to
concerns associated with protein
production. Therefore, EPA is proposing
that, under § 174.27(c)(2), a PVCP-PIP
would also meet § 174.27(c) if:
hsrobinson on PROD1PC76 with PROPOSALS2
The Agency determines after review that
the genetic material that encodes the
pesticidal substance or leads to the
production of the pesticidal substance:
(i) Encodes a protein that is minimally
modified from a coat protein from a virus
that naturally infects plants, or
(ii) Produces no protein.
EPA developed the criterion in
§ 174.27(c)(2) because the Agency
recognizes that developers may wish to
modify PVCP-PIP constructs to achieve
certain product development goals such
as greater efficacy, and such
modifications might result in changes to
the protein(s) produced. Most minor
modifications to the genetic material
would be unlikely to cause changes to
the protein that would be significant
from a human or nontarget organism
perspective. Under § 174.27(c)(2) EPA
may consider such modifications on a
case-by-case basis. Many of the
modifications are likely to produce
proteins that fall within the range of
natural variation of the virus. However,
it is not currently possible to define
clearly the range of variation of viruses
in general or even of any particular
virus as discussed in Unit IV.D. of the
companion document published in
today’s Federal Register. Therefore,
§ 174.27(c)(2)(i) requires an Agency
review to determine qualification.
PVCP-PIPs are known to confer
resistance by two mechanisms.
Resistance may be either proteinmediated, in which the level of
resistance is correlated with the level of
protein expression, or it may be RNAmediated, in which the level of
resistance is not correlated with the
level of protein expression. (See
discussion in Unit II.E.) In the case of
RNA-mediated resistance, little to no
PVC-protein may be produced from the
PVCP-PIP. In such cases, little to no risk
due to protein production would be
associated with the PVCP-PIP. However,
the Agency believes that the only
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• neomycin phosphotransferase II
(NPTII) and the genetic material
necessary for its production,
• phosphomannose isomerase (PMI)
and the genetic material necessary for
its production,
• CP4 enolpyruvylshikimate-3phosphate (CP4 EPSPS) and the genetic
material necessary for its production,
• glyphosate oxidoreductase (GOX or
GOXv247) and the genetic material
necessary for its production, and
• phosphinothricin acetyltransferase
(PAT) and the genetic material
necessary for its production.
Below is a summary of EPA’s finding
that these inert ingredients present a
low risk to human health and the
environment; the docket for this
proposed rule contains the Agency’s full
risk assessment in the document
‘‘Environmental Risk Assessment of
Plant-Incorporated Protectant (PIP) Inert
Ingredients.’’ EPA also proposes to add
to subpart X the partial tetracycline
resistance gene as present under the
control of a bacterial promoter in
papaya line 55–1.
EPA has conducted an environmental
risk assessment of the PIP inert
ingredient phosphinothricin
acetyltransferase (PAT) and the genetic
material necessary for its production.
Topics covered in this assessment
include mode of action, ecological
effects, endangered species
considerations, and gene flow from a
modified plant to wild or weedy
relatives. Data cited in this assessment
were submitted to the Agency in
support of Dekalb’s DBT 418 and Ciba
Seed’s Event 176 Bt corn registrations
and Syngenta’s COT 102 Bt cotton
registration. Ecological data and
published information on the biology of
this protein indicate that this PIP inert
ingredient is not known to be toxic and/
or pathogenic to plant or animal species.
In 1997, the Agency granted a tolerance
exemption for this PIP inert ingredient
in all plants due to the low human
IV. Proposed Exemption for Certain
health risks associated with this protein
Inert Ingredients
(40 CFR 180.1151; 62 FR 17717, April
11, 1997). Based on all of its
As noted in Unit II.F. of this
assessments, EPA has determined that
preamble, one of the general
this inert ingredient will pose low
qualifications for exemption at § 174.21
ecological and occupational risk.
is that ‘‘any inert ingredient that is part
EPA has conducted an environmental
of the plant-incorporated protectant is
risk assessment of the PIP inert
on the list codified at §§ 174.485
ingredient CP4 enolpyruvylshikimate-3through 174.490.’’ EPA is proposing to
phosphate synthase (CP4 EPSPS) and
add several substances to § 174.486
the genetic material necessary for its
when they are used in a PIP that is listed production. Topics covered in this
in 40 CFR part 174 subpart B assessment include mode of action,
Exemptions and are in a plant that
ecological effects, endangered species
satisfies § 174.27(a):
considerations, and gene flow from a
modified crop to wild or weedy
• beta-D-glucuronidase (GUS) from
Escherichia coli and the genetic material relatives. Data cited in this assessment
were submitted to the Agency in
necessary for its production,
conditions that can a priori indicate
there will be no protein production are
encompassed by the criterion in
§ 174.27(c)(1). Any other type of
construct that may confer RNAmediated resistance through PTGS
would be reviewed by the Agency under
the criterion in § 174.27(c)(2)(ii). A
PVCP-PIP would meet § 174.27(c) if EPA
determines that no PVC-protein is
produced from the PVCP-PIP.
If protein is produced, today’s
proposed exemption would cover only
those PVC-proteins that are not
significantly different from naturally
occurring plant viral coat proteins, i.e.,
proteins that are virtually unmodified or
minimally modified. For more
significantly modified PVC-proteins, the
base of experience upon which EPA
relies for support of the proposed
exemption would not be applicable.
Therefore, EPA would not be able to
make the determination a priori as part
of this proposed rule that the PVCP-PIP
poses a low probability of risk to
humans and the environment and will
not generally cause unreasonable
adverse effects on the environment even
in the absence of regulatory oversight
under FIFRA. However, such PVCP-PIPs
may still be eligible for registration, and
any significantly modified PVC-proteins
could be evaluated as part of the
registration review (as discussed in Unit
II.G.). (For discussion of the concept of
‘‘minimally modified’’ see Unit IV.E.2.
of the companion proposed exemption
published in today’s Federal Register.)
3. Historical approaches. EPA’s
current proposed approach is consistent
with what EPA has always intended.
EPA has never intended that any
proposed exemption for PVCP-PIPs
would cover those PIPs that produce
proteins significantly different from
those that occur naturally (November
23, 1994, 59 FR at 60524; July 19, 2001,
66 FR 37865 and 66 FR 37796).
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support of Monsanto’s MON 810 Bt
Corn registration. Ecological data and
published information on the biology of
this protein indicate that this PIP inert
ingredient is not known to be toxic and/
or pathogenic to plant or animal species.
In 1996, the Agency granted a tolerance
exemption for this PIP inert ingredient
in all plants due to the low human
health risks associated with this protein
(40 CFR 180.1174; 61 FR 40338, August
2, 1996). Based on all of its assessments,
EPA has determined that this inert
ingredient will pose low ecological and
occupational risk.
EPA has conducted an environmental
risk assessment of the PIP inert
ingredient glyphosate oxidoreductase
(GOX) and the genetic material
necessary for its production. Topics
covered in this assessment include
mode of action, ecological effects,
endangered species considerations, and
gene flow from a modified crop to wild
or weedy relatives. Data cited in this
assessment were submitted to the
Agency in support of Monsanto’s MON
810 Bt Corn registration. Ecological data
and published information on the
biology of this protein indicate that this
PIP inert ingredient is not known to be
toxic and/or pathogenic to plant or
animal species. In 1997, the Agency
granted a tolerance exemption for this
PIP inert ingredient in all plants due to
the low human health risks associated
with this protein (40 CFR 180.1190; 62
FR 52505, October 8, 1997). Based on all
of its assessments, EPA has determined
that this inert ingredient will pose low
ecological and occupational risk.
EPA has conducted an environmental
risk assessment of the PIP inert
ingredient neomycin
phosphotransferase II (NPTII) and the
genetic material necessary for its
production. Topics covered in this
assessment include mode of action,
ecological effects, endangered species
considerations, and gene flow from a
modified crop to wild or weedy
relatives. Data cited in this assessment
were submitted to the Agency in
support of Monsanto’s NewLeaf Potato
and YieldGard Plus Corn registrations
and is discussed in more detail in the
Bacillus thuringiensis PlantIncorporated Protectant and MON 863
Biopesticide Registration Action
Documents (Ref. 123). Ecological data
and published information on the
biology of this protein indicate that this
PIP inert ingredient is not known to be
toxic and/or pathogenic to plant or
animal species. In 1994, the Agency
granted a tolerance exemption for this
PIP inert ingredient in all plants due to
the low human health risks associated
with this protein (40 CFR 180.1134; 59
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FR 49351, September 28, 1994). Based
on all of its assessments, EPA has
determined that this inert ingredient
will pose low ecological and
occupational risk.
EPA has conducted an environmental
risk assessment of the Escherichia coliderived PIP inert ingredient beta-Dglucuronidase (GUS) and the genetic
material necessary for its production.
Topics covered in this assessment
include mode of action, ecological
effects, endangered species
considerations, and gene flow from a
modified crop to wild or weedy
relatives. Data cited in this assessment
were submitted to the Agency in
support of Monsanto’s Bollgard II Bt
cotton registration and are discussed in
the Bollgard II Biopesticide Registration
Action Document (Ref. 124). Ecological
data and published information on the
biology of this protein indicate that this
PIP inert ingredient is not known to be
toxic and/or pathogenic to plant or
animal species. In 2001, the Agency
granted a tolerance exemption for this
PIP inert ingredient in all plants due to
the low human health risks associated
with this protein (40 CFR 180.1216; 66
FR 42957, August 16, 2001). Based on
all of its assessments, EPA has
determined that this inert ingredient
will pose low ecological and
occupational risk.
EPA has conducted an environmental
risk assessment of the Escherichia coliderived PIP inert ingredient
phosphomannose isomerase (PMI) and
the genetic material necessary for its
production. Topics covered in this
assessment include mode of action,
ecological effects, endangered species
considerations, and gene flow from a
modified crop to wild or weedy
relatives. Data cited in this assessment
were submitted to the Agency in
support of Syngenta’s MIR604 Bt corn
registration. Ecological data and
published information on the biology of
this protein indicate that this PIP inert
ingredient is not known to be toxic and/
or pathogenic to plant or animal species.
In 2004, the Agency granted a tolerance
exemption for this PIP inert ingredient
in all plants due to the low human
health risks associated with this protein
(40 CFR 180.1252; 69 FR 26770, May 14,
2004). Based on all of its assessments,
EPA has determined that this inert
ingredient will pose low ecological and
occupational risk.
EPA believes the partial tetracycline
resistance gene as present in papaya line
55–1 presents low risk to human health
and the environment and could also be
added to 40 CFR part 174 subpart X. No
protein is expected to be produced from
the gene because it is under the control
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19623
of a prokaryotic promoter and is only a
partial gene that is not expected to
function in plants (Ref. 125). Therefore,
no ecological or human health effects
would be associated with this inert
ingredient as found in papaya line 55–
1 because it consists of only DNA.
Transfer of an antibiotic resistance
marker gene from plants to
microorganisms in the gut or in the
environment may theoretically be
possible, but it is extremely unlikely
(Refs. 126 and 127). In addition, because
only a portion of the tetracycline
resistance gene is present in papaya line
55–1, if any horizontal gene transfer of
this genetic material were to occur, it
would be unlikely to confer antibiotic
resistance to any organism that acquired
it (Ref. 125).
EPA asked the 2005 SAP to comment
on the Agency’s environmental risk
assessment for the first six of these
selectable markers. The Panel
concluded that the ‘‘antibiotic resistance
marker (NPTII) and other markers (GUS
and PMI) should be exempt provided
they were in the plant species
determined to be of low risk using
criteria’’ the SAP proposed as discussed
in Unit III.C.2.i. (Ref. 11) and EPA relied
on, as appropriate, in developing the list
comprising § 174.27(a)(1). In addition,
the Panel concluded that the ‘‘herbicide
markers (CP4 EPSPS, GOX/GOXv247
and PAT) should not be exempted, but
rather should be considered on a caseby-case basis taking into consideration
the potential that the crop plant has to
become feral’’ (Ref. 11). EPA notes,
however, that the only crop plants that
will be included on the list comprising
§ 174.27(a)(1) are those whose potential
to become feral has been considered.
Thus, EPA’s inclusion of these six
selectable markers in 40 CFR part 174
subpart X - List of Approved Inert
Ingredients when they are used in PIPs
as inert ingredients in a plant that
satisfies § 174.27(a) is consistent with
the 2005 SAP’s recommendations
regarding these inert ingredients.
EPA is also considering an alternative
under which NPTII, GUS, and PMI
would be exempt from FIFRA when
used as inert ingredients with any
exempt PIP, regardless of the plant in
which they are expressed. Although the
SAP recommended that they only be
exempt provided they were used in a
plant species determined to be of low
risk based on the considerations
encompassed in § 174.27(a), the Panel
did not provide a rationale as to why the
markers would not be considered low
risk in other plants as well. Given that
these markers are widespread in the
environment and would be expected to
confer no particular selective advantage
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hsrobinson on PROD1PC76 with PROPOSALS2
on any plant in the environment that
might express them, the Agency knows
of no rationale why this limitation
would be necessary. The Agency
believes that its risk assessment would
support such an exemption for these
inert ingredients.
EPA is also proposing a technical
correction to § 174.480 to make the
language consistent with the general
requirements for exemption, which
recognize that for some PIPs no FFDCA
tolerance may be required. In such
cases, it is not necessary that the inert
ingredients have been exempted from
FFDCA section 408 requirements.
V. Economic Analysis
Virus infection is a serious problem in
agricultural production. Virtually every
plant species is susceptible to infection
by at least one of more than 500 known
plant viruses (Ref. 6). Particular crop or
weed hosts are nearly always infected
by certain plant viruses under natural
conditions (Ref. 103). Plant viruses
create economic losses for a vast variety
of crops by reducing yields and
negatively affecting the quality of the
crop, damaging fruits, leaves, seeds,
flowers, stems, and/or roots (Refs. 103
and 128). Symptom development and
vector transmission rates are affected by
the environment and so can vary across
locations or seasons (Ref. 103).
Virus diseases have often resulted in
devastating agricultural losses, at times
destroying entire plantings of crops in
certain locations (Ref. 103). For
example, more than 100 million citrus
trees had been destroyed by citrus
tristeza virus (CTV) by 1991 in citrus
growing regions around the world,
including California (Ref. 129). CTV is
one of the most economically important
viruses because of its widespread
distribution, the severity of damage
caused by infection, and the long life
span of individual trees (Ref. 130).
Growers may need to use several
control methods during a crop season in
an attempt to prevent viral infection and
dissemination, primarily by planting
virus-free material for mechanically
transmitted viruses. For vectortransmitted viruses, control measures
have often focused on chemical
insecticides, fungicides, and
nematicides to reduce the population of
vectors that transmit viruses from plant
to plant. However, control of vectors is
not always feasible or effective as a way
to control virus transmission (Ref. 103).
In another common control strategy,
crops are grown in rotation with crops
that the virus does not infect to reduce
the virus load in the field. This method
has serious limitations as well. In some
cases, the development of resistant
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cultivars can be the only viable means
of virus control. Plants developed
through conventional breeding
techniques offer some degree of virus
resistance. However, breeding for
resistance has not been successful for
the majority of field crops that are
severely affected by viruses (Ref. 128).
In some agricultural regions, some crop
species cannot be grown effectively
because of the persistent presence of
infected plant populations and/or
potential virus vectors (Ref. 103).
Contrary to traditional control measures,
transgenic virus-resistant crops offer an
effective means of virus protection.
This proposed rule would benefit the
public by ensuring protection of human
health and the environment while also
reducing the cost of and time needed for
regulatory review of transgenic virusresistant crops. This proposal would
also help to appropriately allocate
Federal resources for risk evaluation by
focusing Agency attention on those
PVCP-PIPs that warrant review. This
proposed rule would also benefit the
industry by removing regulatory
uncertainty for this class of products.
This economic analysis (EA) prepared
for this proposed rule estimates the
projected compliance cost for the
industry under the baseline of full
registration for all PVCP-PIPs and
compares that to the compliance cost for
the potentially affected industry under
the proposed rule in order to estimate
the expected savings from the regulation
relief. The steps used to obtain a cost
estimate for the proposed rule are
summarized below.
Since the nature and timing of future
development of PVCP-PIPs are
unknown, the EA begins by identifying
nine case studies that represent the
broadest range of PVCP-PIPs that the
Agency anticipates could be developed
in the future. After considering the
characteristics of the products that have
already been marketed, characteristics
of the crop plants that have been the
subject of field trials for PVCP-PIPs, and
knowledge of the field of genetically
engineered virus-resistant crops, EPA
estimated the percentage of products
projected to be characterized by each
case study, i.e., the ‘‘prevalence’’ of the
case study. The stated prevalence
represents the best estimate of the
expectation of a PVCP-PIP product like
the one in a specific case study being
developed in the future.
For each case study, a set of data
would be required of a developer in
order to register the PVCP-PIP. The cost
and burden of potential data
requirements for each case study under
the baseline are compared with the
potential data requirement costs and
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burden under the proposed option.
Using the prevalence for each case
study, EPA estimated the probability of
developing a PVCP-PIP product like that
examined in any of the case studies in
any year, given that the Agency
anticipates 1.5–2.5 PVCP-PIPs being
developed each year over a 10–year
period. These probabilities determine
the frequency and timing of
development and registration of PVCPPIPs in a model EPA designed to
compute compliance cost savings.
To estimate compliance cost savings
in any year, the number of PVCP-PIPs
like the one developed in a given case
study was multiplied by the difference
between cost and burden under the
proposed rule and baseline. Since the
model made use of probabilities, the
average of 5,000 simulations was
computed for each year to represent the
annual compliance cost savings for the
proposed rule. Using this procedure, the
estimated annual impact, based on
average cost estimates per data
requirement, is expected to result in a
regulatory compliance cost reduction
approximately within the range of
$340,000 and $360,000 a year. Over a
10–year period, the annual average
regulatory compliance cost reduction is
expected to be approximately $350,000.
The potential exemptions under the
proposed rule, as compared to the
baseline under which no PVCP-PIPs are
exempted, would reduce regulatory
costs for the potentially affected
industry and the EPA, remove
regulatory uncertainty for industry, and
provide important information to the
public regarding the safety of exempted
PVCP-PIPs. Entities that may benefit
from the proposed rule and alternative
options are the public, companies that
develop and market PVCP-PIPs
(applicants and/or registrants), farmers,
and the environment. However,
potential future benefits to these entities
are difficult to quantify due to data
limitations and uncertain market
conditions. In addition, considerable
difficulty exists in quantitatively
evaluating non-market benefits, such as
reduced environmental and human
health risks, consistency of regulation,
reduced regulatory uncertainty, and
improvements in public perception of
biotechnology products.
VI. Preliminary Statutory Finding
A. What Risk Assessment Methodology
did EPA use for this Proposed Rule?
Generally, when EPA assesses the
risks caused by the use of a pesticide,
it considers both the potential hazard
that the pesticide poses to the
environment and the potential for
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exposure to the pesticide due to its use.
For most pesticides (e.g., chemical
pesticides), EPA relies on data generated
by laboratory testing using
representative animal models to
estimate hazard endpoints. To develop
exposure estimates the Agency
evaluates other information including
product characterization data, proposed
use patterns, and information generated
from mathematical models. Exposure
and hazard estimates are combined to
quantify the potential risk associated
with the pesticide’s use. The data
requirements describing the types of
information to be generated and other
guidance for assessing risk are detailed
in 40 CFR part 158.
The questions posed as part of the risk
assessment in evaluating most
pesticides (e.g., biological or chemical
pesticides) can also be posed for the
PVCP-PIPs that are exempted in this
proposed action, and 40 CFR part 158
can be used as guidance. EPA adopted
an approach for evaluating the potential
risks of PVCP-PIPs that is consistent
with the unique characteristics of
pesticides produced and used in a living
plant and the scientific knowledge and
experience accumulated on these
substances.
To address the hazard endpoints
described in 40 CFR part 158 for the
PVCP-PIPs that qualify for this proposed
exemption, EPA relied on a very large
body of information in the public
literature that was developed through
many decades of testing and
observation. EPA thus did not need to
rely on animal model testing for
assessing risk as it would for most other
pesticides (e.g., chemical pesticides)
where specific hazard data are lacking.
In addition, PIPs are produced within
the living plant, and the pesticidal
substance is used in situ in the plant.
Exposure to PVCP-PIPs is therefore
limited relative to exposure to chemical
pesticides that are applied broadly in
the environment, e.g., through aerial
application.
1. Large body of knowledge and
experience exists. Typically, in
assessing a pesticide for environmental
risk, EPA considers data fulfilling the
information requirements posed in 40
CFR part 158 to evaluate the potential
effect of the pesticide on birds,
mammals, freshwater fish and
invertebrates, estuarine and marine
animals, and nontarget plants and
insects (e.g., predators, parasites, and
pollinators). For most pesticides, this
information must be generated using
animal models. To address these same
questions for the PVCP-PIPs that are the
subject of this proposed exemption, EPA
was able to rely on a long history of
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hundreds, if not thousands of years of
natural exposure to plant virus coat
proteins by nontarget organisms. EPA
relies on these experiences and the
scientific literature generated by a
century of food safety studies (Refs. 131
and 132) to assess the PVCP-PIPs that
are the subject of these exemptions.
EPA also took into account the large
and varied information base available in
the public scientific literature from a
number of disciplines including plant
genetics, plant physiology, plant
virology, weed science, molecular
biology, biochemistry, ecology, and
plant breeding. For example, the Agency
used experimental data derived from the
science of plant pathology to
characterize the pest resistance
mechanisms in plants (Ref. 56) and
relied on the scientific knowledge base
of plant virology and virus ecology to
evaluate how plant viruses interact with
each other and with the plant during
infection (Ref. 60).
2. PVCP-PIPs are produced within the
living plant, and the pesticidal
substance is used in situ in the plant,
affecting the exposure paradigm. EPA
used information from the fields of
plant pathology, biochemistry,
microbial ecology, and ecology in
considering all aspects of risk, including
exposure. PVCP-PIPs are produced
within the living plant itself, and the
pesticidal substance is used in situ in
the plant to protect against pests, in
contrast to most other pesticides, which
must be applied to or near the plant.
Because a PVCP-PIP is produced and
used within the plant, physiological
constraints limit the amount of
pesticidal substance produced by the
plant. Regardless of the tissues
containing the PVCP-PIP or the level at
which PVC-protein is expressed, the
PVCP-PIP, including any PVC-protein,
is contained within the plant parts.
Therefore, the routes by which other
organisms may be exposed to the PVCPPIP may be more limited, e.g., dietary
exposure is likely to be the predominant
route of exposure, and physical contact
with the plant or plant parts will
generally be necessary for exposure to
occur.
The PVCP-PIPs exempted by this
proposed rule are biotic and are subject
to the processes of biodegradation and
decay that all such materials undergo
(Ref. 133). Biotic materials are broken
down to constituent parts through the
enzymatic processes of living
organisms, and these constituent parts
are used as building blocks during
growth of other biotic substances. In
addition, PVCP-PIPs are biodegradable
to their constituent elements through
catabolism by living organisms. Because
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of their biodegradable nature, PVCPPIPs do not bioaccumulate (i.e., build
up in tissues because the body is unable
to either break the substance down or
eliminate it) or biomagnify (i.e.,
progressively build up in successive
trophic levels because it bioaccumulates
in the bodies of organisms lower in the
food chain). Because of these
characteristics, the potential for new
exposures to occur beyond direct
physical exposures to the plant or plant
parts is limited.
A question directly affecting the
exposure component of the risk
assessment that has no equivalent in the
assessment of more traditional
pesticides (e.g., chemical pesticides)
must be posed for PIPs. Because PIPs are
produced and used in the living plant,
the possibility that the ability to
produce a PIP may be transferred by
outcrossing and hybridization from the
crop plant to a wild or weedy relative
was considered. A large volume of
information is available in the public
literature to assess the risks of gene flow
generally (Refs. 19 and 134) and for
PVCP-PIPs in particular (Refs. 12, 32,
36, 135, 136, 137, 138, 139, and 140).
B. Exemption Determination for PVCPPIPs, Including Certain Inert Ingredients
EPA preliminarily concludes that
PVCP-PIPs that meet the criteria
specified in this proposed action
warrant exemption under FIFRA section
25(b)(2). The use of PVCP-PIPs that meet
the criteria in 40 CFR 174.21, including
the criteria proposed in this Federal
Register to be inserted at 40 CFR 174.27
poses a low probability of risk to the
environment and is not likely to cause
unreasonable adverse effects in the
absence of regulatory oversight. EPA
bases this preliminary conclusion upon
an evaluation of the potential risks that
use of PVCP-PIPs qualifying for this
exemption would reasonably pose to
man and the environment, and upon an
evaluation of whether their use causes
unreasonable adverse effects. EPA
preliminarily concludes that PVCP-PIPs
qualifying for this exemption pose a low
probability of risk to the environment as
demonstrated by information from the
fields of plant genetics, plant
physiology, plant virology, weed
science, molecular biology,
biochemistry, ecology, and plant
breeding; from many years of experience
growing and consuming plants that
contain coat proteins from plant viruses;
and from Agency knowledge about
horticultural and agricultural practices.
EPA also believes that use of these
plant-incorporated protectants in food is
safe under the FFDCA section 408
standard as explained in the preamble
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to this document and the companion
document published elsewhere in this
issue of the Federal Register exempting
residues of the PVC-protein portion of a
PVCP-PIP.
EPA believes that PVCP-PIPs that
meet the criteria in 40 CFR 174.21,
including the criteria proposed in this
Federal Register to be added at 40 CFR
§ 174.27, are also not likely to cause
unreasonable adverse effects, even in
the absence of regulatory oversight. As
a result, EPA concludes that PVCP-PIPs
qualifying for this exemption do not
cause any unreasonable adverse effects
with respect to human dietary risk.
Taking into account the economic,
social, and environmental costs and
benefits of the use of such products, as
discussed in the preamble and
associated Economic Analysis (found in
the docket for this rulemaking), EPA
believes that the low levels of risks that
such products present do not justify the
cost of regulating such products. Note
that products that qualify for this
exemption would remain subject to the
requirement for submission of
information regarding adverse effects
under 40 CFR 174.71. Even though EPA
believes the probability is very low that
risks would arise with the PVCP-PIPs
qualifying for this exemption, the
adverse effects reporting requirement
will alert the Agency should any such
rare circumstances occur. EPA could
then address such instances, as
appropriate, under FIFRA.
VII. Request for Comment
EPA requests comment on whether
the Agency has appropriately identified
in this proposed exemption those PVCPPIPs that are of a nature not requiring
regulation under FIFRA. In particular,
the Agency requests comment on the
following specific issues:
1. EPA requests comment on whether
additional plants could be appropriately
included in the list of plants comprising
proposed § 174.27(a)(1) because they
would present low risk with respect to
concerns associated with weediness of
the plant itself and any wild or weedy
relatives of the plant if it were to
contain any PVCP-PIP. For example, the
2004 SAP identified the following
plants that are not included in proposed
§ 174.27(a)(1): almond (Prunus
communis), apricot (Prunus armeniaca),
cape daisy (Osteospermum spp.),
chrysanthemum (Dendranthema spp.),
celery (Apium graveolens), eggplant
(Solanum melongena), geranium
(Pelargonium spp.), hyacinth
(Hyacinthus spp.), guava (Psidium
guajava), kiwi (Actinidia spp.),
nectarine and peach (Prunus persica),
okra (Abelmoschus esculentus), olive
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(Olea europaea), parsley (Petroselinum
crispum), petunia (Petunia spp.),
pistachio (Pistacia vera), plum (Prunus
domestica), spinach (Spinacia oleracea),
taro (Colocasia esculenta), tomato
(Solanum lycopersicum), watermelon
(Citrullus lanatus), and wishbone flower
(Torenia spp.).
EPA would be particularly interested
in information about these plants or
others that addresses the questions in
Unit III.C.2.i. that EPA posed to crop
experts as part of its evaluation as to
whether specific species should be
included on the list. In some cases, EPA
has already consulted with one or more
experts for these plants, but the Agency
does not believe it has the information
necessary to draw a conclusion for these
plants. Given the reliance on expert
opinion to make these determinations,
EPA would like to have responses from
at least three experts for any given crop
before including it on the list at
§ 174.27(a)(1). In other cases, EPA
completed at least three consultations,
but the Agency received information
from at least one expert suggesting that
the plant may not meet the low risk
standard for inclusion in the
§ 174.27(a)(1) list, e.g., because of
questions about the formation of viable
hybrids in nature with wild or weedy
relatives or questions about the
propensity of the crop to naturalize.
EPA describes its analyses in the
following paragraphs and requests
assistance from the public on the issues
raised.
EPA is inclined to include almond
(Prunus communis) on the list in
§ 174.27(a)(1) on the basis of
information received from expert
consultations. However, EPA is seeking
any information from the public that
would enable the Agency to complete
its assessment of the potential for a
PVCP-PIP to introgress into a population
of a wild or weedy relative or a
naturalized population of the species
and what effect such introgression
might have. Specifically, the experts
indicated that natural hybrids may be
able to form with some other stone fruit
trees (Ref. 42). However, if such trees
are likely to be found in commercial
cultivation, natural hybrids would not
necessarily be expected in areas outside
of managed orchards. Regarding
whether almond is a weedy species,
both experts mentioned that almond
forms feral populations. However, they
have not usually required weed
management activity because ‘‘the trees
are infrequent and tend to be seen as
beneficial’’ (Ref. 42). One expert said,
‘‘Almond is not highly susceptible to
viruses affecting other Prunus tree crop
species. Thus virus resistance is not a
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major determinate of feral almond
fitness in current environments.... Thus,
it is likely that transgenic resistance
would not greatly benefit either
commercial or feral almonds’’ (Ref. 42).
EPA is inclined to include amaryllis
(Hippeastrum spp.) on the list in
§ 174.27(a)(1) on the basis of
information received from consultations
with amaryllis experts that EPA
conducted upon recommendation from
other experts in flower breeding.
However, EPA is seeking any
information from the public that would
enable the Agency to complete its
assessment of the weedy characteristics
of amaryllis and the potential for gene
exchange between feral and cultivated
populations. Two experts indicated that
there are no wild or weedy relatives in
the United States with which amaryllis
can form viable hybrids in nature,
although one expert said, ‘‘Hippeastrum
puniceum (Lam.) Kuntze is naturalized
in Puerto Rico, the Virgin Islands,
Louisiana and Hawaii. Hippeastrum
puniceum is a diploid species that is
occasionally used in breeding programs.
In controlled crosses, it will breed with
other diploid species, and is probably
represented in modern Hippeastrum
cultivars. However, most modern
Hippeastrum cultivars available in the
florist and greenhouse trade are
complex, tetraploid hybrids that are
difficult to backcross to H. puniceum’’
(Ref. 42). One expert believed that no
species in the genus are known to
become feral or easily spread into noncrop areas. However, the others noted
that this occasionally occurs without
requiring weed management activity.
One said, ‘‘Hippeastrum puniceum may
have been introduced into Puerto Rico,
possibly during pre-Colombian times,
and it has since sparingly naturalized....
Spread is slow and minimal and has not
required management activity’’ (Ref. 42).
Another said, ‘‘Plants generally
naturalize in disturbed areas along
roadsides and irrigation ditches. The
species is self-incompatible, but can
form seed in naturalized settings. The
plants also reproduce asexually via offsets. Long distance dispersal appears
minimal. Hippeastrum puniceum is
considered a low-risk introduced plant
in Hawaii and appears that it does not
require active weed-management’’ (Ref.
42). All three experts agreed that it was
unlikely acquisition of virus resistance
would cause amaryllis to become feral
or easily spread into non-crop areas in
the United States. For example, one
expert said, ‘‘Hippeastrum has been
grown commercial outdoors since the
early 1900’s in semi-tropical areas of the
US (Hippeastrum is not winter-hardy).
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There has not been a single record of
any plants escaping and becoming feral.
There is no reason to believe that
acquiring transgenic resistance to one or
more viruses would increase the ability
of plants to become feral or easily
spread into non-crop areas’’ (Ref. 42).
EPA is inclined to include apricot
(Prunus armeniaca) on the list in
§ 174.27(a)(1) on the basis of
information received from expert
consultations. However, EPA is seeking
any information from the public that
would enable the Agency to complete
its assessment of the potential for a
PVCP-PIP to introgress into a population
of a wild or weedy relative or a
naturalized population of the species.
Specifically, two experts indicated that
apricot may be able to cross with plum
species because ‘‘[i]f planted in close
proximity apricot can be crossed by bees
to Japanese plums. That suggests the
same could happen with native US
plum species, of which there are many
in the eastern US’’ (Ref. 42). However,
both experts suggested that the
frequency of hybrid production would
be extremely low. Two experts
indicated that apricot is not known to
become feral or easily spread into noncrop areas, while the third expert said
that he has ‘‘seen rare plants in
[Michigan] that are feral or left-over
homeowner trees. They did not appear
to spread as the big seeds mostly drop
under the trees and seem not very
competitive compared to the weeds’’
(Ref. 42). All of the experts agreed that
acquisition of virus resistance would be
unlikely to change apricot’s propensity
to become feral. According to one
expert, ‘‘It is not likely that this would
occur because climatic conditions and
the occurrence of fungal and bacterial
diseases are more limiting than the
viruses’’ (Ref. 42).
EPA believes that more information
about cape daisy (Osteospermum spp.)
is needed to address issues raised by
expert consultation. EPA is seeking any
information from the public that would
enable the Agency to complete its
assessment of the potential for a PVCPPIP to enhance the potential of species
in this genus to naturalize. One expert
indicated, ‘‘Osteospermum fruticosum
is a low-risk naturalized plant in
Hawaii, and is also found, along with O.
ecklonis, in California. Other
Osteospermum species have naturalized
in Australia and New Zealand. The
genus is endemic to the Cape Floristic
Region of southern Africa which has a
Mediterranean climate. Thus, there is
potential for more species of
Osteospermum to naturalize in
California which, like Australia and
New Zealand, has a Mediterranean
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climate.... Transgenic or not,
Osteosperum [sic] has potential to
further naturalize in Mediterranean
climates and needs further monitoring
for invasive potential in these areas’’
(Ref. 42). However, the other two
experts indicated that it was unlikely
that virus resistance would cause cape
daisy to become feral or easily spread
into non-crop areas. One said, ‘‘Other
factors are much more likely to limit its
invasive potential, such as available
moisture, presence of competing
vegetation, and predation by insects and
vertebrates. Viruses do not appear to be
limiting its spread’’ (Ref. 42). The other
expert said, ‘‘Viral resistance could
conceivably increase fecundity and
spread, but there is no data to confirm
or refute the possibility’’ (Ref. 42).
EPA is inclined to include
chrysanthemum (Dendranthema spp.)
on the list in § 174.27(a)(1) on the basis
of information received from
consultations with two chrysanthemum
experts. These experts indicated that
there are no wild or weedy relatives in
the United States with which
commercial chrysanthemum can form
viable hybrids in nature. One expert
believed that no species in the genus are
known to become feral or easily spread
into non-crop areas, while the other
noted that this has occurred rarely in
California, Ohio, Pennsylvania, and
Massachusetts. Nevertheless, these
populations have not required weed
management activity because they
‘‘have remained small consisting of only
a few plants’’ (Ref. 42). Both experts
believed it unlikely that acquired virus
resistance could lead to commercial
chrysanthemum becoming feral or easily
spreading into non-crop areas. One
expert said, ‘‘Plants in the genus
Dendranthema are generally not easily
propagated by seed, and are vegatatively
[sic] propagated by cuttings or division.
They do not compete well with other
plants and do not persist in untended
garden situations, and would certainly
not do so in non-crop areas’’ (Ref. 42).
EPA has received one response from
an eggplant expert suggesting that
eggplant (Solanum melongena) meets
the requirements for inclusion on the
list in § 174.27(a)(1). This consultation
indicates that eggplant meets the three
conditions outlined above by the SAP:
it does not have wild or weedy relatives
in the United States with which it can
form viable hybrids in nature, it is not
currently weedy or invasive in the
United States, and there is no reason to
believe that acquisition of virus
resistance would make eggplant weedy
or invasive. The expert said, ‘‘Similar to
other species where wild relatives have
been utilized to enhance the cultivated
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form of the crop, genes for improved
fitness are derived from the wild
relative. Neither the disease resistant
wild relative nor the improved cultivars
have shown a propensity to become
feral’’ (Ref. 42). EPA is seeking public
comment on this determination because
the Agency desires a more robust
response base.
EPA believes that more information
about geranium (Pelargonium spp.) is
needed to address issues raised by
expert consultation. EPA is seeking any
information from the public that would
enable the Agency to complete its
assessment of the potential for a PVCPPIP to spread to a wild or weedy
population in the United States or
enhance the potential of species in this
genus to naturalize. Regarding the
potential for spread to a wild or weedy
population, two experts indicated that
species within this genus do not form
viable hybrids in nature with wild or
weedy relatives in the United States, but
a third expert said, ‘‘In the wild, P.
cucullatum will hybridize with P.
betulinum (L.) L’Her. and P. patulum
Jacq. Pelargonium grandiflorum forms
natural hybrids with P. sublignosum
Knuth. The extent to which these
hybridizations and other hybridizations
occur is not well known’’ (Ref. 42).
Regarding the weedy tendencies of this
genus, one expert indicated that ‘‘nine
species are reported as naturalized or
persistent in California... but most
occupy disturbed sites near cultivated
or urbanized areas’’ (Ref. 42). Another
expert said, ‘‘It seems possible that in
Mediterranean climates Pelargonium
could become a weed problem’’ (Ref.
42). Two other experts thought that
acquisition of virus resistance would
not affect the weedy tendencies of this
genus. One said, ‘‘Pelargonium species
are notoriously poor seed producers and
are all also native to Africa, particularly
South Africa. They have specialized
ecological niches that would not easily
be available anywhere in the U.S. or its
territories. California is the most likely
place where this could happen, and no
incidence of an adventive Pelargonium
has ever been reported. Viral resistance
would not mitigate these factors that
prevent adventive establishment’’ (Ref.
42).
EPA is inclined to include hyacinth
(Hyacinthus spp.) on the list in
§ 174.27(a)(1) on the basis of
information received from consultations
with hyacinth experts. However, EPA is
seeking any information from the public
that would enable the Agency to
complete its assessment of the potential
for hyacinth to naturalize. Three experts
consulted indicated that this genus does
not form viable hybrids in nature with
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wild or weedy relatives in the United
States. Two experts indicated that there
are no naturalized species of Hyacinthus
in the United States, although a third
said, ‘‘Hyacinthus orientalis has been
reported as naturalized in the Blackland
Prairies of Texas,’’ but details were not
available (Ref. 42). All three experts
agreed that acquired virus resistance is
unlikely to make hyacinth become feral
or spread into non-crop areas.
On the basis of expert consultation,
EPA has concluded that guava (Psidium
guajava) does not meet the low risk
standard needed for inclusion on the
§ 174.27(a)(1) list. Two experts
indicated that more research is needed
to establish the potential for outcrossing
with wild or weedy relatives. All three
experts reported that guava is known to
become feral or easily spread into noncrop areas in the United States. One
expert stated, ‘‘Guava is a vigorous,
common, weed in both warm to cool
climates. It would likely give this plant
additional competitive advantage with
transgenic resistance to viruses’’ (Ref.
42). However, another expert believed
that ‘‘[g]uava is easily spread without
having transgenic resistance. It does not
appear that containing resistance to one
or more virus [sic] would enhance its
ability to become feral’’ (Ref. 42). EPA
requests commenters who believe guava
would be appropriate to include on the
list in § 174.27(a)(1) specifically to
address whether there are wild or
weedy relatives with which guava could
form viable hybrids in nature in the
United States (including Puerto Rico,
the Virgin Islands, Guam, the Trust
Territory of the Pacific Islands, and
American Samoa) and to address the
concern that guava is a weedy species
and acquisition of virus resistance could
exacerbate these tendencies. Please
provide literature citations or other
evidence to support any claims contrary
to EPA’s expert consultations.
EPA believes that more information
about lily (Lilium spp.) is needed to
address issues raised by expert
consultation conducted after
recommendation from other flower
experts. EPA is seeking any information
from the public that would enable the
Agency to complete its assessment of
the potential for lily to become feral or
spread into non-crop areas and the
impact that acquired virus resistance
might have on this potential. The
experts agreed that in the United States
the likelihood of a species in the genus
Lilium forming viable hybrids in nature
with a wild or weedy relative was very
small given that lilies do not cross
readily. ‘‘This is especially true for the
hybrids that are adapted or selected for
the intensive greenhouse or irrigated
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gardens’ environment. These lilies do
not form successful colonies outside
these specific environments. The chance
that genes will be transferred from
gardens to wild populations is
negligible’’ (Ref. 42). However,
regarding the weedy tendencies of this
genus, one expert said ‘‘Several species
of Asian or European origin are
sporadically naturalized following
escape from cultivation, but none strays
far or is widespread or common enough
to be considered a pest.... Lilium
longiflorum (Easter lily; Japan) has been
recorded from Utah and Florida’’ (Ref.
42). Another expert said, ‘‘Lilium
[formosanum] (Taiwan lily) has been
known to invade natural habitats in
Northern and Eastern Australia....
Caution would be advised in
introducing L. [formosanum] into... the
US’’ (Ref. 42). Two experts believed it
unlikely that acquired virus resistance
would affect the likelihood of lilies
becoming feral, although a third said,
‘‘Virus resistance might increase the
speed and degree with which these
exotic species might naturalize’’ (Ref.
42).
EPA is inclined to include nectarine
and peach (Prunus persica) on the list
in § 174.27(a)(1) on the basis of
information received from expert
consultations. However, EPA is seeking
any information from the public that
would enable the Agency to complete
its assessment of the potential for a
PVCP-PIP to introgress into a population
of a wild or weedy relative or a
naturalized population of the species
and what effect such introgression
might have. Specifically, the experts
indicated that natural hybrids may be
able to form with some other stone fruit
trees (Ref. 42). However, if such trees
are likely to be found in commercial
cultivation, natural hybrids would not
necessarily be expected in areas outside
of managed orchards. Regarding
whether Prunus persica is a weedy
species, three of the four experts
mentioned that nectarines and peaches
are able to form feral populations (Ref.
42). Nevertheless, three of the four
experts indicated that they believed it
would be unlikely that Prunus persica’s
weedy tendencies, if any, would be
exacerbated if it acquired transgenic
resistance to one or more viruses. One
expert said, ‘‘Generally the viruses are
not the limiting factor to the
establishment of feral peaches. The
limiting factors are fungal and bacterial
diseases that kill the plants before they
can reproduce’’ (Ref. 42). The fourth
expert said, ‘‘I would expect that the
acquisition of virus resistance would
enhance the spread of feral populations
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but would suggest that other causes of
death, such as peach tree short life,
bacterial canker and Armillaria Root
Rot, are likely to be a more significant
limitation to the spread and longevity of
a feral nectarine tree’’ (Ref. 42).
EPA believes that more information
about olive (Olea europaea) is needed to
address issues raised during expert
consultation. Two experts indicated that
hybridization with a wild or weedy
relative has not been documented in the
United States (Ref. 42). Both of these
experts indicated that olive can
naturalize. However, they disagreed
about the frequency with which this is
likely to occur. One expert suggested
olive frequently forms reproducing and
sustaining populations in non-crop
areas and that it was ‘‘highly likely’’ that
olive would become feral or easily
spread into non-crop areas if it acquired
transgenic resistance to one or more
viruses because ‘‘O. europaea seeds are
very viable and dispersed by rodents’’
(Ref. 42). However, another said, ‘‘It is
highly unlikely that olives would
become strongly feral or widely spread
because the seeds are infrequently
spread far from the tree, have a low
reproduction rate due to poor seed
germination and have a high rate of feral
seedling mortality. Further, as a slow
growing tree olives do not spread
rapidly’’ (Ref. 42). The 2005 SAP also
commented on including olives in the
list of plants in § 174.27(a)(1). They
noted olives have reportedly formed
‘‘feral olive infestations in the Channel
Islands National Park, and in oak
woodlands and forest on Sonoma Valley
and Davis, CA. In California, olive is
‘considered an invasive exotic’ that
‘compete[s] with native flora’ (personal
communication)’’ (Ref. 42). EPA
believes that before olive could be
added to the list of plants in
§ 174.27(a)(1), the Agency would need
information to resolve the question of
how weedy olive is in the United States
and the effect virus resistance would
have on any feral populations of olive
that could acquire a PVCP-PIP from
cultivated olive.
EPA has received one response from
a parsley expert suggesting that parsley
(Petroselinum crispum) meets the
requirements for inclusion on the list in
§ 174.27(a)(1). This consultation
indicates that parsley meets the three
conditions outlined above by the SAP:
it does not have wild or weedy relatives
in the United States with which it can
form viable hybrids in nature, it is not
currently weedy or invasive in the
United States, and there is no reason to
believe that acquisition of virus
resistance would make parsley weedy or
invasive. The breeder noted that parsley
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could form viable hybrids with feral
populations of parsley, but ‘‘parsley
populations are generally quite shortlived away from cultivation and
typically are not self-sustaining’’ (Ref.
42). He also noted, ‘‘I would not expect
parsley to become more easily spread
with the acquisition of virus resistance.
Although I’m aware that parsley is a
host to celery mosaic virus and carrot
motley dwarf, I have not known these
viruses to be common limiting factors in
parsley growth or reproduction, at least
not here at our genebank in Iowa.
Fungal diseases and insects are much
more important’’ (Ref. 42). EPA is
seeking public comment on this
determination because the Agency
desires a more robust response base.
EPA is inclined to include petunia
(Petunia spp.) on the list in
§ 174.27(a)(1) on the basis of
information received from consultations
with petunia experts. However, EPA is
seeking any information from the public
that would enable the Agency to
complete its assessment of the weedy
characteristics of petunia and the
likelihood that acquired virus resistance
could cause petunia to become feral or
easily spread into non-crop areas. The
experts indicated that this genus does
not form viable hybrids in nature with
wild or weedy relatives in the United
States. However, two of the three
experts indicated that petunia has
formed reproducing and sustaining
populations in non-crop areas while
noting that such populations have not
required weed management activity. All
three experts indicated that acquired
virus resistance is unlikely to change
the status quo. However, one noted that,
‘‘as viruses affect petunia vigor,
resistance might conceivably increase
the odds’’ (Ref. 42).
EPA is inclined to include pistachio
(Pistacia vera) on the list in 174.27(a)(1)
on the basis of information received
from two expert consultations.
However, EPA is seeking any
information from the public that would
enable the Agency to complete its
assessment of the potential for a PVCPPIP to introgress into a population of a
wild or weedy relative or a naturalized
population of the species and what the
impact of acquired virus resistance is
likely to be. Specifically, the experts
indicated several crosses have been
reported in the literature, suggesting
‘‘that potentially P. vera genes can
eventually be transmitted to other
species in the form of gene flow.’’
However, hybrids are only rarely formed
as ‘‘they are isolated phenologically....’’
Nevertheless, one expert also indicated,
‘‘There are a lot of unknowns in the
phenology and cross-compatibility of
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different species of pistachio’’ (Ref. 42).
Both experts indicated that ferality in
pistachio is rare. One suggested it was
not possible to say what the likelihood
would be that pistachio would become
feral or easily spread into non-crop
areas if it acquired transgenic virus
resistance. However the other said, ‘‘It is
very unlikely pistachio would be widely
feral as the primary method of spread,
drop from the tree, results in a large
percentage (>95%) of the nuts
degrading, so they do not sprout.
Further, the nuts do not go a long
distance when they drop, localizing
spread if sprouting does occur. Finally,
if birds do remove a nut with a viable
embryo from the tree they generally
destroy it by eating...’’ (Ref. 42).
EPA is inclined to include plum
(Prunus domestica) on the list in
§ 174.27(a)(1) on the basis of
information received from expert
consultations. However, EPA is seeking
any information from the public that
would enable the Agency to complete
its assessment of the potential for a
PVCP-PIP to introgress into a population
of a wild or weedy relative or a
naturalized population of the species.
Specifically, the experts indicated that
several native plum species occur in the
United States. However, one indicated
that because ‘‘P. domestica is a
hexaploid, it would not cross with
native Prunus plum species, which are
all diploid’’ (Ref. 42). In addition, if any
hybrids between cultivated plum and
wild American plum species did occur,
they ‘‘would not be fertile because of the
chromosome number difference.’’ EPA
thus believes that the risk of
introgressing a PVCP-PIP into a wild or
weedy population through gene transfer
in the United States is very low.
Regarding whether plum is a weedy
species, one expert mentioned that
although he had not personally
observed it, he ‘‘heard from others that
domestica... [is] found naturalized
particularly in New England and
Oregon. Some of these species tend to
be easily spread by root suckers, and are
better able to compete as weeds. Likely
they only survive on roadsides and
unmanaged areas, and could be easily
killed if desired’’ (Ref. 42). Nevertheless,
all three of the experts indicated that
they believed it would be unlikely that
plum’s weedy tendencies, if any, would
be exacerbated if it acquired transgenic
resistance to one or more viruses.
According to one expert, ‘‘I doubt
viruses are the only thing which
restricts domestica from spreading more
than it already has’’ (Ref. 42). According
to another, ‘‘Currently virus diseases are
not the most important limiting diseases
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for plum in the U.S. Other fungal and
bacterial diseases are the limiting factors
and cause death of uncared for
commercial plums. Therefore transgenic
plums with virus resistance would still
be very susceptible to these limiting
fungal and bacterial diseases’’ (Ref. 42).
EPA has received one response from
a spinach expert suggesting that spinach
(Spinacia oleracea) meets the
requirements for inclusion on the list in
§ 174.27(a)(1). This consultation
indicated that spinach meets the three
conditions outlined above by the SAP:
it does not have wild or weedy relatives
in the United States with which it can
form viable hybrids in nature, it is not
currently weedy or invasive in the
United States, and there is no reason to
believe that acquisition of virus
resistance would make spinach weedy
or invasive. The expert noted,
‘‘Transgenic viral resistance alone
probably would not make spinach
survive wild conditions, because there
are other fungus (e.g. downy mildew,
Stemphylium leaf spot) diseases and
bacterial diseases (e.g. bacterial leaf
spot), as well as drought resistance and
competing ability issues’’ (Ref. 42). EPA
is seeking public comment on this
determination because the Agency
desires a more robust response base.
EPA believes that more information
about taro (Colocasia esculenta) is
needed to address issues raised by
expert consultation. For example,
although experts knew of no weedy
relatives with which taro might cross,
‘‘crossing is theoretically possible
among all of the taros’’ (Ref. 42). One
expert indicated that ‘‘taro can flower
naturally in places such as Kula in
Maui, Hawaii. The climate there allows
taro to flower naturally, whereas in
other places it is often necessary to
induce flowering with hormone
applications. Furthermore, hybrids
made by cross-fertilization are viable. It
is entirely possible for taro to survive in
the wild in tropical and subtropical
climates. Most taros would succumb
because taro has been cultivated for so
long that it is mostly dependent on
humans to compete with many weeds.
By itself it is almost always outcompeted by weeds and dies out. But
theoretically it can survive, it can crosspollinate and form viable progeny’’ (Ref.
42). Regarding whether taro is known to
become feral or easily spread in noncrop areas, one expert said, ‘‘YES, but
only in favorable conditions of adequate
warmth and moisture.’’ Another expert
indicated that ‘‘taro is considered an
invasive species in certain places
(Florida)’’ (Ref. 42). Regarding whether
acquired transgenic resistance to one or
more viruses could change taro in this
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respect, the experts disagreed. One
expert said, ‘‘It is highly unlikely that
taro with acquired transgenic resistance
would spread to non-crop areas because
the probability of crossing is extremely
small. Through vegetative propagation it
will require man intervention just as
non-transgenic plants.’’ Another expert
said, ‘‘Taro has many pests, including
viruses, that restricts [sic] its ability to
compete with more weedy plant
species. Resistance to any of these pests
would increase its competitiveness but
this is not likely to turn taro into a weed
problem.’’ However, the third expert
said, ‘‘With resistance to one or more
virus diseases, taro would become
hardier. That is the reason for breeders
to go to the trouble of developing
disease-resistant plants. A hardier taro
is more likely to be successful and
survive as an escaped cultivated
species. It has already been seen that
taro has become feral in certain parts of
Florida. With added resistance, it would
be more likely to survive in the wild,
provided that resistance gives it some
advantage. In other words, if the virus
disease is important, resistance is
valuable. In Thailand, the taro plants
that one can find along roadsides (feral)
possess a high degree of resistance to
taro leaf blight, the most destructive
disease of cultivated taro there. Those
that don’t possess resistance don’t stand
much of a chance to survive on their
own’’ (Ref. 42). EPA believes that before
taro could be added to the list of plants
in § 174.27(a)(1), the Agency would
need information to evaluate the
likelihood that feral populations of taro
could acquire a PVCP-PIP from
cultivated taro and to evaluate whether
acquisition of virus resistance is likely
to increase taro’s likelihood of forming
feral populations.
EPA believes that more information
about tomato (Solanum lycopersicum) is
needed to address issues raised by
several experts that EPA consulted. For
example, three of four experts indicated
that tomato is able to form viable
hybrids in nature in the United States
with its putative progenitor Solanum
lycopersicum var. cerasiforme. These
experts indicated the hybrids formed are
fertile, self-compatible, and freely
intercross due to highly compatible
phenology. However, a third expert
indicated that ‘‘[a]lthough crosses can
occur between wild species and
cultivated tomato, usually with human
intervention, the direction of the cross
is such that the wild species has to be
the male parent.... If the cultivated
tomato has the transgene, transfer to
wild species via pollen will not
happen’’ (Ref. 42). EPA is not however
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interested solely in whether transfer
occurs via pollen, but whether a
transgene could introgress into a wild
population through a hybrid
intermediate. Three of four experts also
indicated that tomato is able to form
feral populations in the United States
(including Puerto Rico, the Virgin
Islands, Guam, the Trust Territory of the
Pacific Islands, and American Samoa),
although one expert pointed out that
neither virus-resistant cultivars nor
resistant wild relatives have
demonstrated a greater propensity to
become feral, suggesting that acquisition
of a PVCP-PIP may not exacerbate
whatever weedy tendencies exist in
tomato. However, another expert
suggested that this question would have
to be tested in the field under controlled
conditions. EPA believes that before
tomato could be added to the list of
plants in § 174.27(a)(1), the Agency
would need information to evaluate the
effect of virus resistance on any wild or
weedy populations of tomato that could
acquire a PVCP-PIP from cultivated
tomato and to evaluate whether
acquisition of virus resistance is likely
to exacerbate tomato’s weedy
tendencies.
EPA believes that more information
about watermelon (Citrullus lanatus) is
needed to address issues raised by
expert consultation. For example,
experts indicated that watermelon is
able to cross with C. lanatus var.
citroides. Moreover, one expert
indicated hybrids made by crossfertilization are sexually fertile and
demonstrate ‘‘[m]ore vigor compared
with cultivated watermelon (C. lanatus
var. lanatus)’’ (Ref. 42). Regarding
whether watermelon is known to
become feral or easily spread in noncrop areas, one expert indicated that
escaped plants are able to form
reproducing and sustaining populations
in non-crop areas, although this occurs
rarely and has not required weed
management activity outside of crop
areas (Ref. 42). Regarding whether
acquired transgenic resistance to one or
more viruses could change watermelon
in this respect, one expert indicated this
was ‘‘[u]nlikely. Watermelons have few
viruses that kill the plant or decrease its
reproductive activity. Therefore, gaining
virus resistance will not likely increase
it’s [sic] reproductive success in feral
populations’’ (Ref. 42). Another expert
said, ‘‘Virus pressure would likely be far
less in feral populations than in
cultivated fields due to differences in
time of germination, rate of growth,
population density, [and] reduced
numbers of aphid vectors’’ (Ref. 42).
EPA believes that before watermelon
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could be added to the list of plants in
§ 174.27(a)(1), the Agency would need
information to evaluate the likelihood
that wild populations of C. lanatus var.
citroides or feral populations of C.
lanatus var. lanatus could acquire a
PVCP-PIP from cultivated watermelon
and what effect this acquisition might
have.
EPA believes that more information
about wishbone flower (Torenia spp.) is
needed to address issues raised by
expert consultation. EPA is seeking any
information from the public that would
enable the Agency to complete its
assessment of the potential for a PVCPPIP to enhance the potential of species
in this genus to naturalize. All three
experts consulted indicated that Torenia
species do not form viable hybrids in
nature with wild or weedy relatives in
the United States. However, all
indicated that Torenia has naturalized
in certain areas of the United States.
One expert said, ‘‘Torenia fournieri has
been reported to naturalize by seed in
Florida and Louisiana, but it is not clear
to what extent. I personally have
observed re-seeding in garden settings.
Given the rising popularity of Torenia in
American horticulture, there is probable
cause for concern in the deep south,
California and Hawaii. However, the
species in cultivation are heat sensitive
and moisture-demanding, which would
probably limit the extent to which they
can naturalize’’ (Ref. 42). Expert
consultations also suggest that not
enough information is known about the
potential of virus resistance to affect the
plant’s weedy tendencies. One expert
said, ‘‘I do not know to what extent
viruses impact Torenia fournieri. It is
conceivable that viral resistance could
increase fecundity’’ (Ref. 42).
EPA is not proposing to include
celery (Apium graveolens), kiwi
(Actinidia spp.), or okra (Abelmoschus
esculentus) on the list in § 174.27(a)
because the Agency was unable to
complete any expert consultations on
these crops. EPA is therefore seeking
information from the public to address
whether such crops could qualify for
inclusion on the list.
EPA also requests comment on the
weediness potential of squash
(Cucurbita pepo) and any wild or weedy
relatives in the United States that could
acquire a PVCP-PIP from cultivated
squash through gene flow.
2. EPA requests comment on the
Agency’s options for the weediness
criterion in § 174.27(a)(2) discussed in
Unit III.C.2.iii. Specifically, the Agency
is considering whether it is more
appropriate to evaluate the potential for
a crop to form ‘‘viable hybrids’’ or
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‘‘viable, fertile hybrids’’ in nature with
a wild or weedy relative.
In addition, EPA is considering
whether it is necessary to evaluate
whether the plant containing the PIP is
unlikely to establish weedy or invasive
populations outside of agricultural
fields in the United States even if the
plant contains a PVCP-PIP, assuming
that the plant has no wild or weedy
relatives in the United States with
which it can form viable hybrids in
nature and it is not a weedy or invasive
species outside of agricultural fields in
the United States.
EPA also requests comment on
language for the criterion in
§ 174.27(a)(2) (e.g., such as under option
four) that would allow EPA to broadly
consider the effect that virus resistance
might have on wild or weedy plant
populations that could acquire the
PVCP-PIP. Under such an approach, the
individual determinations that the
Agency would make would likely
require data to be generated that would
not normally occur as a routine part of
product development (but may be
developed for a review by USDA/
APHIS). Such determinations are likely
to involve similar amounts of effort as
registration reviews, but they would
provide a means whereby a PVCP-PIP
could be exempted even if used in a
plant that has wild or weedy relatives in
the United States. The Agency requests
commenters to indicate how
controversial individual determinations
using such language as under option 4
are likely to be, as the Agency would
like to have an exemption procedure
that requires only one public notice (see
Unit III.A.2.).
3. EPA requests comment on the
merits of incorporating the use of
biocontainment and/or bioconfinement
techniques into § 174.27(a), such that
PVCP-PIPs deployed in tandem with
such technology could be determined to
meet the weediness criterion. Please see
the discussion of this option in Unit
III.C.3., which articulates several issues
associated with such an option and
suggests regulatory language that might
be used.
4. EPA requests comment on the
Agency’s use of the term ‘‘weedy.’’ EPA
uses the term in two different contexts:
in ‘‘wild or weedy relatives’’ and in
‘‘weedy or invasive species.’’ However,
the Agency notes that the term has a
different meaning in each context.
When discussing a ‘‘wild or weedy
relative,’’ EPA considers weedy plants
to be those with the characteristics of
weeds, i.e., those that are considered
undesirable, unattractive, or
troublesome, especially when growing
where they are not wanted. However,
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when discussing ‘‘weedy or invasive
species,’’ EPA considers a weedy
species to be a species that is an
aggressive competitor in natural
ecosystems. EPA recognizes that it
would be better to have a single
definition of the term ‘‘weedy,’’ but the
Agency believes both meanings of the
term ‘‘weedy’’ are in common, scientific
usage. In addition, the Agency is not
aware of a term other than ‘‘wild or
weedy relative’’ that would encompass
all plants that grow outside of
agricultural fields, or a term other than
‘‘weedy or invasive species’’ that would
encompass all of the plants that are
problematic from a management
perspective. EPA would be particularly
interested in alternative suggestions to
describe each of these situations and
thus enable the Agency to avoid using
two different meanings for the word
‘‘weedy.’’
5. EPA requests comment on whether
the viral interactions criterion in
§ 174.27(b)(1)(i) could be expanded to
read ‘‘the viral pathotype used to create
the PVCP-PIP has naturally infected
plants in the United States or other
parts of North America and naturally
infects plants of the same species as
those containing the PVCP-PIP.’’ EPA
recognizes that viruses are likely to
move freely across political boundaries.
Thus, limiting this criterion to viruses
that have naturally infected plants ‘‘in
the United States or other parts of North
America’’ may be most appropriate
limitation for avoiding the introduction
of sequences from an exotic virus into
the United States through creation of a
PVCP-PIP.
6. EPA requests comment on whether
it is necessary for the Agency to address
viral interactions, i.e., recombination, as
articulated in § 174.27(b), in order for
the Agency to conclude that a PVCP-PIP
is low risk. EPA requests commenters to
indicate whether their comments apply
to RNA viruses, DNA viruses, or both.
The Agency notes that a large number
of PVCP-PIPs are likely to meet
§ 174.27(b) as proposed. EPA therefore
requests commenters who believe
§ 174.27(b) is unnecessary to focus their
remarks on why those PVCP-PIPs that
do not meet the conditions of proposed
§ 174.27(b) would pose low risk with
respect to recombination rather than
addressing the average risk associated
with PVCP-PIPs as a whole.
For the PVCP-PIPs that would only
qualify for an exemption without the
limitations provided by § 174.27(b), EPA
does not believe the Agency can
conclude low risk with respect to
recombination (as the Agency must do
in order to remove § 174.27(b) entirely)
because the 2004 and 2005 SAPs have
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identified specific instances where this
general conclusion may not hold.
Nevertheless, EPA is considering
removing this criterion in whole or in
part if the Agency receives information
suggesting that such factors as
articulated and as incorporated into
§ 174.27(b) are unnecessary for
concluding a particular PVCP-PIP is low
risk. For example, the Agency notes that
the current global movement of goods
and people likely results in the at least
occasional transport of plant viruses
great distances from their original
geographic distribution in spite of
governmental efforts to limit their
movement. In such a context, the
Agency questions the relevance of
requiring as a condition of exemption
that the viral pathotype used to create
the PVCP-PIP has naturally infected
plants in the United States.
7. EPA requests comment on whether
the protein production criterion in
§ 174.27(c)(1)(i) could be modified to
encompass other types of PVCP-PIP
constructs that mediate resistance based
on PTGS. According to today’s proposal,
any such constructs other than those
inserted only in an inverted repeat
orientation or lacking a start codon
would be reviewed by the Agency for
lack of protein production under
§ 174.27(c)(2). However, if the Agency
could identify additional types of
constructs that would present
reasonable assurance that no protein
would be produced in any plant tissues
at any point in the plant’s
developmental cycle, including if PTGS
were to be suppressed, such constructs
could be included under
§ 174.27(c)(1)(i) and would not require
Agency review to verify that no protein
would be produced.
8. EPA requests comment on whether
the Agency could extend the proposed
exemption (including regulatory text
and rationale as written) to other PIPs
that are based on any plant virus gene
that confers virus resistance when no
protein is produced from the inserted
virus sequence because it is inserted
only in an inverted repeat orientation
and/or it lacks an initiation codon for
protein synthesis. The 2005 SAP noted
that ‘‘[o]ther PIPs conferring virus
resistance should be evaluated similarly
as are the PVCP-PIPs, if the PIPs mode
of action is via PTGS’’ (Ref. 11).
However, the Panel also mentioned
several risk concerns associated with
specific virus proteins. The Agency
therefore concluded that PTGS was a
necessary but not sufficient condition
for expanding the exemption to other
types of virus gene-based PIPs given that
protein can be produced under certain
circumstances from many constructs
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that employ PTGS, and the Agency does
not currently have sufficient
information to conclude that such
protein would pose low risk to the
environment. In the case of the two
types of inserts described above, the
2005 SAP indicated that it could be
‘‘safely determined’’ that no protein
would ever be produced from such
constructs (Ref. 11), and they would
meet § 174.27(b) and (c). Section
174.27(a) would be evaluated as it is
evaluated for PVCP-PIPs given that the
relevant consideration would be the
virus-resistant phenotype of the plant
rather than the means by which the trait
is conferred. EPA thus believes that the
criteria in today’s proposed exemption
address all relevant risk considerations
for PIPs based on any plant virus gene
when no protein is produced from the
inserted virus sequence. EPA is
therefore inclined to expand the
exemption to include PIPs based on any
viral gene that confers virus resistance
if the PIP meets § 174.27(a) and no
protein is produced from the inserted
virus sequence because it is inserted
only in an inverted repeat orientation
and/or it lacks an initiation codon for
protein synthesis.
9. EPA requests comment on the
alternative approach the Agency is
considering for exempting marker genes
that are used as inert ingredients with
PIPs under which NPTII, GUS, and PMI
would be exempt from FIFRA when
used as inert ingredients with any
exempt PIP, regardless of the plant in
which they are expressed (as discussed
in Unit IV).
10. EPA requests comment on the
possibility of developing an Agencydetermined approach for exempting
inert ingredients under FIFRA. Under
this approach, EPA would propose new
language at 40 CFR 174.21(c) that would
enable the Agency to review inert
ingredients on a case-by-case basis to
determine whether they meet the
standard established for inert
ingredients in 40 CFR part 174 subpart
X-List of Approved Inert Ingredients.
EPA is considering such a procedure to
ensure that a low-risk PVCP-PIP that
otherwise meets the conditions for
exemption at § 174.21 would not require
a FIFRA registration solely due to the
presence of an inert ingredient that may
prove to be low risk upon review. The
only alternative to registration for such
a PVCP-PIP would be to add the inert
ingredient to the list through
rulemaking under FIFRA section 25(b),
such that the PVCP-PIP could be
exempted. Rulemaking would take
considerably longer than an Agency
determination procedure like that
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described in today’s proposal for other
exemption criteria.
The criteria that EPA is considering
for determining whether an inert
ingredient would be exempt under an
Agency determination are:
i. The inert ingredient is non-toxic to
humans and animals and does not
produce a toxic substance,
ii. The inert ingredient is nonallergenic, and
iii. If the inert ingredient is an
antibiotic resistance gene or marker
protein, therapy with antibiotics would
not be compromised even if the gene
were to be transferred from plants to
microorganisms in the gut of man or
animal, or in the environment.
11. EPA requests comment on the
Agency’s assumption in the economic
analysis for this proposed rule that the
estimated number of PVCP-PIPs
submitted for regulatory review will be
the same per year over the next 10 years.
EPA assumed a uniform distribution
given that the Agency lacks reliable
information on which to base a more
complex distribution pattern. EPA is
particularly interested in any data or
information supporting a different
assumption for the economic analysis.
12. EPA requests comment on the
usefulness of a guidance document that
would provide a simplified description
of the final rule. EPA intends to develop
such a document and is interested to
know what specific content the public
would find most helpful.
VIII. References
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reports were used in preparing this
proposed rule and are cited in this
document by the number indicated.
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94. Osbourn, J.K., Sarkar, S., Wilson,
T.M.A. Complementation of coat
protein-defective TMV mutants in
transgenic tobacco plants expressing
TMV coat protein. Virology 1990;
179:921–5.
95. Candelier-Harvey, P., Hull, R.
Cucumber mosaic virus genome is
encapsidated in alfalfa mosaic virus coat
protein expressed in transgenic tobacco
plants. Transgenic Research 1993;
2:277–85.
96. Lecoq, H., Ravelonandro, M.,
Wipf-Scheibel, C., Monsion, M., Raccah,
B., Dunez, J. Aphid transmission of a
non-aphid-transmissible strain of
zucchini yellow mosaic potyvirus from
transgenic plants expressing the capsid
protein of plum pox potyvirus.
Molecular Plant-Microbe Interactions
1993; 6:403–6.
97. Maiss, E., Koenig, R., Lesemann,
D.E. Heterologous encapsidation of
viruses in transgenic plants and in
mixed infections. In: Jones, D.D.
Biosafety Results of Field Tests of
Genetically Modified Plants and
Microorganisms. Oakland: University of
California , Division of Agriculture and
Natural Resources, 1994:129–39.
98. Robinson, D.J. Environmental risk
assessment of releases of transgenic
plants containing virus-derived inserts.
Transgenic Research 1996; 5:359–62.
99. Robinson, D.J., Ryabov, E.V., Raj,
S.K., Roberts, I.M., Taliansky, M.E.
Satellite RNA is essential for
encapsidation of groundnut rosette
umbravirus RNA by groundnut rosette
assistor luteovirus coat protein. Virology
1999; 254:105–14.
100. Fuchs, M., Gal-On, A., Raccah,
B., Gonsalves, D. Epidemiology of an
aphid nontransmissible potyvirus in
fields of nontransgenic and coat protein
transgenic squash. Transgenic Research
1999; 8:429–39.
101. Losey, J.E., Eubanks, M.D.
Implications of pea aphid host-plant
specialization for the potential
colonization of vegetables following
post-harvest emigration from forage
crops. Environmental Entomology 2000;
29:1283–8.
102. Vance, V.B., Berger, P.H.,
Carrington, J.C., Hunt, A.G., Shi, X.M. 5’
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proximal potyviral sequences mediate
potato virus X/potyviral synergistic
disease in transgenic tobacco. Virology
1995; 206:583–90.
103. OECD Environment Directorate.
Consensus document on general
information concerning the biosafety of
crop plants made virus resistant through
coat protein gene-mediated protection.
https://www.olis.oecd.org/olis/
1996doc.nsf/
62f30f71be4ed8a24125669e003b5f73/
ce3a104b8ada9e8ac12563e2003183bb/
$FILE/11E63213.ENG. 1996.
104. Miller, W.A., Koev, G., Mohan,
B.R. Are there risks associated with
transgenic resistance to luteoviruses?
Plant Disease 1997; 81:700–10.
105. Pruss, G.J., Ge, X., Shi, X.M.,
Carrington, J.C., Vance, V.B. Plant viral
synergism: the potyviral genome
encodes a broad-range pathogenicity
enhancer that transactivates replication
of heterologous viruses. The Plant Cell
1997; 9:859–68.
´
106. Garcıa-Arenal, F., Malpica, J.M.,
Fraile, A. Evolution of plant virus
populations: The role of genetic
exchange. In: Fairbairn, C., Scoles, G.,
McHughen, A. Proceedings of the 6th
International Symposium on the
Biosafety of Genetically Modified
Organisms. Saskatoon, Canada:
University Extension Press, University
of Saskatchewan, 2000:91–6.
107. Thomas, P.E., Hassan, S.,
Kaniewski, W.K., Lawson, E.C.,
Zalewski, J.C. A search for evidence of
virus/transgene interactions in potatoes
transformed with the potato leafroll
virus replicase and coat protein genes.
Molecular Breeding 1998; 4:407–17.
108. Fuchs, M., Klas, F.E., McFerson,
J.R., Gonsalves, D. Transgenic melon
and squash expressing coat protein
genes of aphid-borne viruses do not
assist the spread of an aphid nontransmissible strain of cucumber mosaic
virus in the field. Transgenic Research
1998; 7:449–62.
109. Lin, H.X., Rubio, L., Smythe, A.,
Jiminez, M., Falk, B.W. Genetic
diversity and biological variation among
California isolates of Cucumber mosaic
virus. Journal of General Virology 2003;
84:249–58.
110. Vigne, E., Komar, V., Fuchs, M.
Field safety assessment of
recombination in transgenic grapevines
expressing the coat protein gene of
Grapevine fanleaf virus. Transgenic
Research 2004; 13:165–79.
111. Allison, R.F., Schneider, W.L.,
Greene, A.E. Recombination in plants
expressing viral transgenes. Seminars in
Virology 1996; 7:417–22.
112. Rovere, C.V., del Vas, M., Hopp,
H.E. RNA-mediated virus resistance.
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Current Opinion in Biotechnology 2002;
13:167–72.
113. Allison, R.F., Schneider, W.L.,
Deng, M. Risk assessment of virus
resistant transgenic plants. In:
Schiemann, J. The Biosafety Results of
Field Tests of Genetically Modified
Plants and Microorganisms. Berlin:
¨
Biologische Bundesanstalt fur Landund Forstwirtschaft, 2000:186–8.
114. Dinant, S., Blaise, F., Kusiak, C.,
Astier-Manifacier, S., Albouy, J.
Heterologous resistance to potato virus
Y in transgenic tobacco plants
expressing the coat protein gene of
lettuce mosaic potyvirus.
Phytopathology 1993; 83:819–24.
115. Teycheney, P.Y., Aaziz, R.,
´
Dinant, S., Salanki, K., Tourneur, C.,
´
Balazs, E. et al. Synthesis of (-)-strand
RNA from the 3’ untranslated region of
plant viral genomes expressed in
transgenic plants upon infection with
related viruses. Journal of General
Virology 2000; 81:1121–6.
116. AIBS. Transgenic virus-resistant
plants and new plant viruses. https://
www.aphis.usda.gov/ppq/biotech/virus/
95_virusrept.pdf. 1995.
117. Greene, A.E., Allison, R.F.
Deletions in the 3’ untranslated region
of cowpea chlorotic mottle virus
transgene reduce recovery of
recombinant viruses in transgenic
plants. Virology 1996; 225:231–4.
118. Nagy, P.D., Ogiela, C., Bujarski,
J.J. Mapping sequences active in
homologous RNA recombination in
brome mosaic virus: prediction of
recombination hot spots. Virology 1999;
254:92–104.
119. Miller, W.A., Koev, G., Beckett,
R. Issues surrounding transgenic
resistance to the Luteoviridae. In:
Schiemann, J. The Biosafety Results of
Field Tests of Genetically Modified
Plants and Microorganisms. Berlin:
¨
Biologische Bundesanstalt fur Landund Forstwirtschaft, 2000:203–9.
120. Nagy, P.D., Zhang, C., Simon,
A.E. Dissecting RNA recombination in
vitro: role of RNA sequences and the
viral replicase. The EMBO Journal 1998;
17:2392–403.
121. Gibbs, M. Risks in using
transgenic plants? Science 1994;
264:1650–1.
122. Hull, R. Risks in using transgenic
plants? Science 1994; 264:1649–50.
123. U.S. Environmental Protection
Agency. Bacillus thuringiensis Cry3Bb1
Protein and the Genetic Material
Necessary for its Production (Vector
ZMIR13L) in Event MON863 Corn
(006484) Biopesticide Registration
Action Document (BRAD). https://
www.epa.gov/pesticides/biopesticides/
ingredients/tech_docs/
brad_006484.htm. 2003.
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124. U.S. Environmental Protection
Agency. Biopesticides Registration
Action Document (BRAD)—Bacillus
thuringiensis Cry2Ab2 protein and its
genetic material necessary for its
production in cotton. https://
www.epa.gov/pesticides/biopesticides/
ingredients/tech_docs/brad_006487.pdf.
2002.
125. Gonsalves, D., Manshardt, R.
Petition 96–051–01p for Determination
of Regulatory Status: Transgenic Papaya
lines 55–1 and their Derivatives. 1996.
126. Codex Alimentarius
Commission. Guideline for the Conduct
of Food Safety Assessment of Foods
Derived from Recombinant-DNA Plants.
2003.
127. Smalla, K., Borin, S., Heuer, H.,
Gebhard, F., van Elsas, J.D., Nielsen, K.
Horizontal transfer of antibiotic
resistance genes from transgenic plants
to bacteria — are there new data to fuel
the debate? In: Fairbairn, C., Scoles, G.,
McHughen, A. Proceedings of the 6th
International Symposium on the
Biosafety of Genetically Modified
Organisms. Saskatchewan: University
Extension Press, 2000:146–54.
128. Tolin, S.A. Persistence,
establishment, and mitigation of
phytopathogenic viruses. In: Levin,
M.A., Strauss, H.S. Risk Assessment in
Genetic Engineering. New York:
McGraw-Hill, Inc., 1991:114–39.
129. Abbas, M., Khan, M.M., Mughal,
S.M., Khan, I.A. Prospects of classical
cross protection technique against
Citrus tristeza closterovirus in Pakistan.
Horticultural Science (Prague) 2005;
32:74–83.
130. EPPO/CABI. Quarantine Pests for
Europe, 2nd ed. Wallingford, UK: CABI
International, 1997.
131. International Food Biotechnology
Council. Biotechnologies and food:
Assuring the safety of foods produced
by genetic modification. Regulatory
Toxicology and Pharmacology 1990;
12(3).
132. Quemada, H. Food safety
evaluation of a transgenic squash. OECD
Workshop on Food: Provisional
Proceedings of the Safety Evaluation.
Paris: OECD, 1994:71–9.
133. Berg, J., Tymoczko, J., Stryer, L.,
Clarke, N. Biochemistry, 5th ed. New
York: W. H. Freeman and Company,
2002.
134. Stewart, C.N.Jr., Halfhill, M.D.,
Warwick, S.I. Transgene introgression
from genetically modified crops to their
wild relatives. Nature Reviews Genetics
2003; 4:806–17.
135. Bartsch, D., Brand, U., Morak, C.,
Pohl-Orf, M., Schuphan, I., Ellstrand, N.
Biosafety of hybrids between transgenic
virus-resistant sugar beet and swiss
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chard. Ecological Applications 2001;
11:142–7.
136. Spencer, L.J., Snow, A.A.
Fecundity of transgenic wild-crop
hybrids of Cucurbita pepo
(Cucurbitaceae): implications for cropto-wild gene flow. Heredity 2001;
86:694–702.
137. Ilardi, V., Barba, M. Assessment
of functional transgene flow in tomato
fields. Molecular Breeding 2001; 8:311–
5.
138. Fuchs, M., Chirco, E.M.,
Gonsalves, D. Movement of coat protein
genes from a commercial virus-resistant
transgenic squash into a wild relative.
Environmental Biosafety Research 2004;
3:5–16.
139. Bartsch, D. Ecological impact of
transgenic virus-resistance in crop,
weed, and wild plant populations (due
to potential alterations of plant
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invasiveness). In: Tepfer, M., Balazs, E.
Virus-resistant Transgenic Plants:
Potential Ecological Impact. Berlin:
Springer, 1997:107–13.
140. Tepfer, M. Risk assessment of
virus-resistant transgenic plants. Annual
Review of Phytopathology 2002; 40:467–
91.
IX. Content of Official Record
EPA has established an official record
for this rulemaking. The official record
includes all information considered by
EPA in developing this proposed rule
including documents specifically
referenced in this action, any public
comments received during an applicable
comment period, and any other
information related to this action,
including any information claimed as
CBI and any information received in any
of the related dockets mentioned below.
This official record includes all
information physically located in the
dockets described in the following
paragraph, as well as any documents
that are referenced in the documents in
the dockets. The public version of the
official record does not include any
information claimed as CBI.
The complete official record for this
rulemaking includes:
The docket identified by the docket
control number OPP–300370 for the
document entitled ‘‘Proposed Policy:
Plant-Pesticides Subject to the Federal
Insecticide, Fungicide, and Rodenticide
Act and the Federal Food, Drug, and
Cosmetic Act’’ (59 FR 60496, November
23, 1994)(FRL–4755–2).
The docket identified by the docket
control number OPP–300369 for the
document entitled ‘‘Plant-Pesticides
Subject to the Federal Insecticide,
Fungicide and Rodenticide Act;
Proposed Rule’’ (59 FR 60519,
November 23, 1994)(FRL–4755–3).
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The docket identified by the docket
control number OPP–300368 for the
document entitled ‘‘Plant-Pesticides;
Proposed Exemption From the
Requirement of a Tolerance Under the
Federal Food, Drug, and Cosmetic Act’’
(59 FR 60535, November 23, 1994)(FRL–
4758–8).
The docket identified by the docket
control number OPP–300371 for the
document entitled ‘‘Plant-Pesticides;
Proposed Exemption From the
Requirement of a Tolerance Under the
Federal Food, Drug, and Cosmetic Act
for Nucleic Acids Produced in Plants’’
(59 FR 60542, November 23, 1994)(FRL–
4755–5).
The docket identified by the docket
control number OPP–300367 for the
document entitled ‘‘Plant-Pesticides;
Proposed Exemption From the
Requirement of a Tolerance Under the
Federal Food, Drug, and Cosmetic Act
for Viral Coat Proteins Produced in
Plants’’ (59 FR 60545, November 23,
1994)(FRL–4755–4).
The docket identified by the docket
control number OPP–300370A for the
document entitled ‘‘Plant-Pesticide
Subject to the Federal Insecticide,
Fungicide, and Rodenticide Act and the
Federal Food, Drug, and Cosmetic Act;
Reopening of Comment Period’’ (61 FR
37891, July 22, 1996)(FRL–5387–4).
The docket identified by the docket
control number OPP–300368A for the
document entitled ‘‘Plant-Pesticides;
Supplemental Notice of Proposed
Rulemaking’’ (62 FR 27132, May 16,
1997)(FRL–5717–2).
The docket identified by the docket
control number OPP–300371A for the
document entitled ‘‘Plant-Pesticides;
Nucleic Acids; Supplemental Notice of
Proposed Rulemaking’’ (62 FR 27142,
May 16, 1997)(FRL–5716–7).
The docket identified by the docket
control number OPP–300367A for the
document entitled ‘‘Plant-Pesticides;
Viral Coat Proteins; Supplemental
Notice of Proposed Rulemaking’’ (62 FR
27149, May 16, 1997)(FRL–5716–6).
The docket identified by the docket
control number OPP–300369A for the
document entitled ‘‘Plant-Pesticides,
Supplemental Notice of Availability of
Information’’ (64 FR 19958, April 23,
1999)(FRL–6077–6).
The docket identified by the docket
control number OPP–300369B for the
document entitled ‘‘Regulations Under
the Federal Insecticide, Fungicide, and
Rodenticide Act for Plant-Incorporated
Protectants (Formerly Plant-Pesticides)’’
(66 FR 37772, July 19, 2001)(FRL–6057–
7).
The docket identified by the docket
control number OPP–300368 for the
document entitled ‘‘Exemption From
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the Requirement of a Tolerance Under
the Federal Food, Drug, and Cosmetic
Act for Residues Derived through
Conventional Breeding From Sexually
Compatible Plants of Plant-Incorporated
Protectants (Formerly Plant-Pesticides)’’
(66 FR 37830, July 19, 2001)(FRL–6057–
6).
The docket identified by the docket
control number OPP–300371 for the
document entitled ‘‘Exemption From
the Requirement of a Tolerance Under
the Federal Food, Drug, and Cosmetic
Act for Residues of Nucleic Acids that
are Part of Plant-Incorporated
Protectants (Formerly Plant-Pesticides)’’
(66 FR 37817, July 19, 2001)(FRL–6057–
5).
The docket identified by the docket
control number OPP–300370B for the
document entitled ‘‘Plant-Incorporated
Protectants (Formerly Plant-Pesticides),
Supplemental Proposal’’ (66 FR 37855,
July 19, 2001)(FRL–6760–4).
The docket identified by the docket
control number EPA–HQ–OPP–2006–
0643 for the companion document
entitled ‘‘Exemption from the
Requirement of a Tolerance under the
Federal Food, Drug, and Cosmetic Act
for Residues of Plant Virus Coat Proteins
that are Part of a Plant-Incorporated
Protectant (PVC-Proteins)’’ (FRL–8100–
5) published elsewhere in this issue of
the Federal Register.
The docket identified by the docket
control number EPA–HQ–OPP–2006–
0642 for this document (FRL–8100–7).
Also included in the complete official
record are:
1. Public comments submitted in
response to the proposals and
supplemental documents cited in the
above paragraph.
2. Reports of all meetings of the
Biotechnology Science Advisory
Committee and the FIFRA Scientific
Advisory Panel pertaining to the
development of this proposed rule.
3. The Economic Analysis for this
proposed rule and supporting
documents.
4. Support documents and reports.
5. Records of all communications
between EPA personnel and persons
outside EPA pertaining to the proposed
rule. (This does not include any interand intra-agency memoranda, unless
specifically noted in the indices of the
dockets).
6. Published literature that is cited in
this document.
X. Statutory and Executive Order
Reviews
A. Executive Order 12866
Pursuant to Executive Order 12866,
entitled Regulatory Planning and
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Review (58 FR 51735, October 4, 1993),
the Office of Management and Budget
(OMB) has determined that this is a
‘‘significant regulatory action’’ because
it may raise potentially novel legal or
policy issues arising out of legal
mandates, the President’s priorities, or
the principles set forth in the Executive
Order. Therefore, this action was
submitted to OMBfor review, and
changes made during that review have
been documented in the docket.
In addition, EPA has prepared an
economic analysis of the impacts related
to this proposed action. The economic
analysis evaluates the
quantifiablebenefits of exempting PVCPPIPs from FIFRA requirements (40 CFR
part174) and discusses the nonquantifiable benefits of this action.
Thiseconomic analysis is contained in a
document entitled ‘‘EconomicAnalysis
for Proposed Exemption Under the
Federal Insecticide,Fungicide, and
Rodenticide Act for Certain PlantIncorporatedProtectants Derived from a
Plant Viral Coat Protein Gene (PVCPPIPs)’’(called here ‘‘the EA’’). This
document is available in thedocket and
is briefly summarized in Unit V.
B. Paperwork Reduction Act
Pursuant to the Paperwork Reduction
Act (PRA), 44 U.S.C. 3501et seq., an
Agency may not conduct or sponsor,
and a person is notrequired to respond
to a collection of information unless it
displays acurrently valid OMB control
number, or is otherwise required to
submitthe specific information by a
statute. The OMB control numbers for
EPA’s regulations codified in Title 40 of
the CFR, after appearing in the preamble
of the final rule, are further displayed
either by publication in the Federal
Register or by other appropriate means,
such as on the related collection
instrument or form, if applicable. The
display of OMB control numbers in
certain EPA regulations is consolidated
in a list at 40 CFR 9.1.
The information collection
requirements contained in thisproposed
rule have been submitted to OMB for
review and approvalunder the PRA in
accordance with the procedures at 5
CFR 1320.11.The burden and costs
related to the information collection
requirementscontained in this rule are
described in an addendum to a
currently approved Information
Collection Request (ICR) identified as
EPA ICR No. 1693.04 (OMB number
2070–0142). As defined in the PRA,
‘‘burden’’ means the total time, effort, or
financial resources expended by persons
to generate, maintain, retain, or disclose
or provide information to or for a
Federal agency. This includes the time
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needed to review instructions; develop,
acquire, install, and utilize technology
and systems for the purposes
ofcollecting, validating, and verifying
information, processing andmaintaining
information, and disclosing and
providing information;adjust the
existing ways to comply with any
previously applicableinstructions and
requirements; train personnel to be able
to respond toa collection of information;
search data sources; complete and
reviewthe collection of information; and
transmit or otherwise disclose
theinformation.
This proposed rule includes
information collection requirements
ofdevelopers who wish to exempt
PVCP-PIPs under the provisions of
theproposed rule. Developers selfdetermining their exemption status
willhave to develop and maintain
records supporting their
determinationand report their
determination to EPA. Developers
relying on Agencydetermination of
exemption status will have to develop
the informationneeded for the Agency
determination and submit it to EPA. The
Agencyhas estimated that this
information collection has an estimated
burdenof 21.5 hours per response for
developer-determined exemptions
and23.5 hours per response for Agencydetermined exemptions. EPAestimates
that there will be one submission of
each type per year fora total annual
respondent burden of 45 hours.
Direct your comments on the
Agency’s need for this information, the
accuracy of the provided burden
estimates, and any suggested methods
for minimizing respondent burden,
including the use of automated
collection techniques, to EPA using the
public docket that has been established
for this proposed rule (Docket ID No.
EPA–HQ–OPP–2006–0642). In addition,
send a copy of your comments about the
ICR to OMB at: Office of Information
and Regulatory Affairs, Office of
Management and Budget, 725 17th St.,
NW., Washington, DC 20503, Attention:
Desk Office for EPA ICR No. 2070–0142.
Since OMB is required to complete its
review of the ICR between 30 and 60
days after April 18, 2007, please submit
your ICR comments for OMB
consideration to OMB by May 18, 2007.
The Agency will consider and address
comments received on theinformation
collection requirements contained in
this proposal whenit develops the final
rule.
C. Regulatory Flexibility Act
Pursuant to section 605(b) of the
Regulatory Flexibility Act (RFA), 5 USC
601 et seq., the Agency hereby certifies
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that this rule will not have a significant
adverse economic impact on a
substantial number of small entities.
For purposes of assessing the impacts
of today’s rule on smallentities, small
entity is defined as: (1) a small business
according tothe small business size
standards established by the U.S. Small
BusinessAdministration (SBA), which
in this case is a pesticides and
agriculturalchemical producer (NAICS
code 325320) with fewer than
500employees; a crop producer (NAICS
code 111) with less than $750,000in
revenues; a college, university, or
professional school (NAICS
code611310) with annual revenues less
than $6.5 million; or an entity
inresearch and development in the
physical, engineering, and lifesciences
(NAICS code 54171) with fewer than
500 employees; (2) asmall governmental
jurisdiction that is a government of a
city, county,town, school district or
special district with a population of less
than50,000; and (3) a small organization
that is any not-for-profit
enterprisewhich is independently
owned and operated and is not
dominant inits field.
In determining whether a rule has a
significant economic impacton a
substantial number of small entities, the
impact of concern is anysignificant
adverse economic impact on small
entities, since the primarypurpose of the
regulatory flexibility analyses is to
identify and addressregulatory
alternatives ‘‘which minimize any
significant economicimpact of the
proposed rule on small entities’’ (5
U.S.C. 603 and 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 regulatory burden or
otherwise has a positive economic effect
on all of the small entities subject to the
rule. This proposed rule will generate
savings by exempting PVCP-PIPs with a
low probability of risk from FIFRA
requirements. Given the overall
potential savings attributed to this rule,
the Agency concludes that this
proposed action will not result in
adverse economic impacts, regardless of
the size of the firm currently developing
and testing PVCP-PIPs or planning to
develop and test PVCP-PIPs. Today’s
action relieves a regulatory burden.
Nevertheless, the Agency continues to
be interestedin the potential impacts of
the proposed rule on small entities
andwelcomes comments on issues
related to such impacts.
D. Unfunded Mandates Reform Act
Under Title II of the Unfunded
Mandates Reform Act of 1995
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(UMRA),Public Law 104–4, EPA has
determined that this action does not
contain a Federal mandate that may
result in expenditures of $100 million or
more forState, local or tribal
governments, in the aggregate, or on the
privatesector in any one year. The
analysis of the cost savings associated
withthis action are described in Unit V
of this preamble. The requirementsof
sections 202, 203, 204 or 205 of UMRA
which relate to regulatoryrequirements
that might significantly or uniquely
affect smallgovernments and to
regulatory proposals that contain a
significantFederal intergovernmental
mandate, respectively, do not apply
totoday’s rule because the rule affects
only the private sector, i.e., personsfield
testing such as universities,
multinational companies,biotechnology
companies, chemical companies, seed
companies;persons selling and
distributing such as multinational
companies,biotechnology companies,
chemical companies, seed companies;
andpersons using PVCP-PIPs such as
farmers.
E. Executive Order 13132
Pursuant to Executive Order 13132,
entitled Federalism (64 FR 43255,
August 10, 1999) EPA has determined
that this proposed rule does not have
federalism implications, because 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. The primary
result of this action is to exempt certain
PVCP-PIPs from most FIFRA
requirements. Thus, the requirements of
section 6 of the Executive Order do not
apply to this rule.
F. Executive Order 13175
Pursuant to Executive Order 13175,
entitled Consultation and Coordination
with Indian Tribal Governments (65 FR
67249, November 9, 2000), EPA has
concluded that this rule does not have
tribal implications because it will not
have any affect on tribal governments,
on the relationship between the Federal
government and the Indian tribes, or on
the distribution of power and
responsibilities between the Federal
government and Indian tribes, as
specified in the Executive Order. EPA is
proposing to exempt certain PVCP-PIPs
from most FIFRA requirements. This is
only expected to affect the private
sector, not tribes or tribal governments.
Thus, Executive Order 13175 does not
apply to this rule.
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G. Executive Order 13211
This rule is not subject to Executive
Order 13211, entitled Actions
Concerning Regulations that
Significantly Affect Energy Supply,
Distribution, or Use (66 FR 28355, May
22, 2001) because it is not designated as
an ‘‘economically significant’’
regulatory action as defined by
Executive Order 12866, nor is it likely
to have any significant adverse effect on
the supply, distribution, or use of
energy.
H. Executive Order 13045
This rule is not subject to Executive
Order 13045, entitled Protection of
Children from Environmental Health
Risks and Safety Risks (62 FR 19885,
April 23, 1997), because because it is
not designated as an ‘‘economically
significant’’ regulatory action as defined
in Executive Order 12866 and because
the Agency does not have reason to
believe that the environmental health or
safety risks addressed by this action
presentdisproportionate risks to
children. The Agency has determined
that thePVCP-PIPs that would be
exempted by this rule pose only a
lowprobability of risk to human health,
including the health of infants
andchildren, and that there is a
reasonable certainty no harm will
resultto infants and children from
aggregate exposure to residues of
thesePVCP-PIPs in food. Existing
information suggests there are
nodisproportionate effects on infants or
children from dietary or otherexposures.
EPA’s assessment and the results of its
assessment arecontained in Unit VIII of
the companion document
publishedelsewhere in this issue of the
Federal Register exempting from the
FFDCA section 408 requirement of a
tolerance, residues of the plantvirus coat
protein portion of a PVCP-PIP.
I. National Technology Transfer
Advancement Act
This rule does not involve a
regulatory action that would requirethe
Agency to consider voluntary consensus
standards pursuant tosection 12(d) of
the National Technology Transfer and
AdvancementAct of 1995 (NTTAA), (15
U.S.C. 272 note). Section 12(d) directs
EPA to use voluntary consensus
standards in its regulatory activities
unless to do so would be inconsistent
with applicable law or otherwise
impractical. Voluntaryconsensus
standards are technical standards (e.g.,
materials specifications, test methods,
sampling procedures, business
practices, etc.) that are developed or
adopted by voluntary consensus
E:\FR\FM\18APP2.SGM
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standards bodies. The NTTAA requires
EPA to provide Congress, through OMB,
explanations when the Agency decides
not to use available and applicable
voluntary consensus standards when
the NTTAA directs the Agency to do so.
J. Executive Order 12898
Pursuant to Executive Order 12898,
entitled Federal Actions to Address
Environmental Justice in Minority
Populations and LowIncomePopulations (59 FR 7629,
February 16, 1994), EPA has
consideredenvironmental justice related
issues with regard to the potential
impactsof this action on the
environmental and health conditions in
low incomeand minority communities.
The Agency is required to considerthe
potential for differential impacts on
sensitive sub-populations.
EPAconsidered available information on
the sensitivities of subgroups aspertains
to the exemptions. EPA concluded that
no subgroup would bedifferentially
affected. See also the companion
document ‘‘Exemptionfrom the
Requirement of a Tolerance under the
Federal Food, Drug, andCosmetic Act
for Residues of Plant Virus Coat Proteins
that are Partof a Plant-Incorporated
Protectant (PVC-Proteins)’’ published
elsewherein this issue of the Federal
Register.
XI. FIFRA Review Requirements
In accordance with FIFRA section
25(d), EPA submitted a draft of
thisproposed rule to the FIFRA
Scientific Advisory Panel, the Secretary
of Agriculture, and to the Committee of
Agriculture of the House of
Representatives and the Committee on
Agriculture, Nutrition, and Forestry of
the Senate.
List of Subjects in 40 CFR Part 174
Environmental protection,
Administrative practice and procedures,
Pesticides and pests.
§ 174.21 General qualifications for
exemptions.
Dated: April 9, 2007.
Stephen L. Johnson,
Administrator.
Therefore, it is proposed that 40 CFR
chapter I be amended as follows:
hsrobinson on PROD1PC76 with PROPOSALS2
PART 174—[AMENDED]
1. The authority citation for part 174
would continue to read as follows:
Authority: 7 U.S.C. 136–136y and 21
U.S.C. 346a and 371.
2. By alphabetically adding to § 174.3
new definitions to read as follows:
§ 174.3
*
*
Definitions.
*
VerDate Aug<31>2005
*
Naturally infect means to infect by
transmission to a plant through direct
plant-to-plant contact (e.g., pollen or
seed), an inanimate object (e.g., farm
machinery), or vector (e.g., arthropod,
nematode, or fungus). It does not
include infection by transmission that
occurs only through intentional human
intervention, e.g., manual infection in a
laboratory or greenhouse setting.
*
*
*
*
*
PVCP-PIP is a plant-incorporated
protectant derived from one or more
genes that encode a coat protein of a
virus that naturally infects plants. This
includes plant-incorporated protectants
derived from one or more plant viral
coat protein genes that produce only
RNA and no virus-related protein.
PVC-protein is the plant virus coat
protein portion of a PVCP-PIP.
*
*
*
*
*
United States means a State, the
District of Columbia, the
Commonwealth of Puerto Rico, the
Virgin Islands, Guam, the Trust
Territory of the PacificIslands, and
American Samoa.
Unmodified means having or coding
for an amino acid sequence that is
identical to an entire coat protein of a
naturally occurring plant virus.
*
*
*
*
*
Virtually unmodified means having or
coding for an amino acid sequence that
is identical to an entire coat protein of
a naturally occurring plant virus, except
for the addition of one or two amino
acids at the N- and/or C-terminus other
than cysteine, asparagines, serine, and
threonine and/or the deletion of one or
two amino acids at the N- and/or Cterminus.
Weedy species means a species that is
an aggressive competitor in natural
ecosystems.
*
*
*
*
*
3. In § 174.21 by revising the
introductory text and paragraph (c) to
read as follows:
*
17:09 Apr 17, 2007
Jkt 211001
A plant-incorporated protectant is
exempt from the requirements of FIFRA,
other than the requirements of § 174.71,
if it meets all of the following criteria.
Plant-incorporated protectants that are
not exempt from the requirements of
FIFRA under this subpart are subject to
all the requirements of FIFRA.
*
*
*
*
*
(c) Any inert ingredient that is part of
the plant-incorporated protectant is on
the list codified at §§ 174.485 through
174.486.
4. By adding § 174.27 to subpart B to
read as follows:
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19639
§ 174.27 Plant-incorporated protectant
derived from a coat protein gene(s) from a
virus(es) that naturally infects plants
(PVCP-PIP).
In order for a plant-incorporated
protectant derived from one or more
genes that encode a coat protein of a
virus that naturally infects plants
(PVCP-PIP) to be exempt, the criteria in
paragraphs (a), (b), and (c) and the
requirements in paragraph (d) of this
section must all be satisfied.
(a) The criterion in paragraph (a) of
this section is satisfied if either
paragraph (a)(1) or paragraph (a)(2) of
this section applies:
(1) The plant containing the PIP is one
of the following: anthurium (Anthurium
spp.), asparagus (Asparagus officinale),
avocado (Persea americana), banana
(Musa acuminata), barley (Hordeum
vulgare), bean (Phaseolus vulgaris),
cacao (Theobroma cacao), carnation
(Dianthus caryophyllus), chickpea
(Cicer arietinum), citrus (Citrus spp.,
e.g., Citrus aurantifolia, Citrus limon,
Citrus paradisii, Citrus sinensis), coffee
(Coffea arabica and Coffea canephora),
corn (Zea maize), cowpea (Vigna
unguiculata), cucumber (Cucumis
sativus), gerbera (Gerbera spp.),
gladiolus (Gladiolus spp.), lentil (Lens
culinaris), mango (Mangifera indica),
orchids (Orchidaceae), papaya (Carica
papaya), pea (Pisum sativum), peanut
(Arachis hypogaea), pineapple (Ananas
comosus), potato (Solanum tuberosum),
soybean (Glycine max), starfruit
(Averrhoa carambola), sugarcane
(Saccharum officinarum), or tulips
(Tulipa spp.).
(2) The Agency determines after
review that the plant containing the PIP
meets paragraphs (a)(2)(i), (a)(2)(ii), and
(a)(2)(iii) of this section:
(i) Has no wild or weedy relatives in
the United States with which it can
form viable hybrids in nature.
(ii) Is not a weedy or invasive species
outside of agricultural fields in the
United States.
(iii) Is unlikely to establish weedy or
invasive populations outside of
agricultural fields in the United States
even if the plant contains a PVCP-PIP.
(b) The criterion in paragraph (b) of
this section is satisfied if either
paragraph (b)(1)(i), paragraph (b)(1)(ii),
or paragraph (b)(2) of this section
applies:
(1)(i) The viral pathotype used to
create the PVCP-PIP has naturally
infected plants in the United States and
naturally infects plants of the same
species as those containing the PVCPPIP, or
(ii) The genetic material that encodes
the pesticidal substance or leads to the
production of the pesticidal substance is
E:\FR\FM\18APP2.SGM
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19640
Federal Register / Vol. 72, No. 74 / Wednesday, April 18, 2007 / Proposed Rules
inserted only in an inverted repeat
orientation or lacking an initiation
codon for protein synthesis such that no
PVC-protein is produced in the plant.
(2) The Agency determines after
review that viruses that naturally infect
the plant containing the PVCP-PIP are
unlikely to acquire the coat protein
sequence through recombination and
produce a viable virus with significantly
different properties than either parent
virus.
(c) The criterion in paragraph (c) of
this section is satisfied if either
paragraph (c)(1) or paragraph (c)(2) of
this section applies:
(1) The genetic material that encodes
the pesticidal substance or leads to the
production of the pesticidal substance:
(i) Is inserted only in an inverted
repeat orientation or lacking an
initiation codon for protein synthesis
such that no PVC-protein is produced in
the plant, or
(ii) Encodes only a single virtually
unmodified viral coat protein. Multiple
PVC-proteins could each separately
meet this criterion. Chimeric PVCproteins do not qualify.
(2) The Agency determines after
review that the genetic material that
encodes the pesticidal substance or
leads to the production of the pesticidal
substance:
(i) Encodes a protein that is minimally
modified from a coat protein from a
virus that naturally infects plants, or
(ii) Produces no protein.
(d)(1) Records to support exemption
determinations made by the developer
of a PVCP-PIP under paragraphs (a)(1),
(b)(1), or (c)(1) of this section; to support
a submission of information under
paragraphs (a)(2), (b)(2), or (c)(2) of this
section; or to support a certification
made by the developer that a PVCP-PIP
meets § 174.21(b) and/or § 174.21(c)
must be maintained by the developer of
the product for the duration of time that
the PVCP-PIP is sold or distributed.
Such records must be made available for
inspection and copying, or otherwise
submitted to the Agency for review
upon request by EPA or its duly
authorized representative.
(2) Information adequate to support
claims for an Agency-determined
exemption must be submitted for review
to the Office of Pesticide Programs,
Attention: PVCP-PIP Exemption.
(3) A statement notifying the Agency
and certifying the accuracy of any
determination made by the developer
that a PVCP-PIP meets § 174.21(b),
§ 174.21(c), paragraph (a)(1) of this
section, paragraph (b)(1) of this section,
and/or paragraph (c)(1) of this section
must be signed by the developer and
submitted to the Office of Pesticide
VerDate Aug<31>2005
17:09 Apr 17, 2007
Jkt 211001
Programs, Attention: PVCP-PIP
Exemption. Any such statement must be
submitted at the time of a first
submission, if any, of information under
paragraph (d)(2) of this section for a
particular PVCP-PIP. If a PVCP-PIP
satisfies paragraphs (a)(1), (b)(1), and
(c)(1)) of this section and §§ 174.21(b)
and (c), the developer must submit a
notification to the Agency of that
determination and certify that the
PVCP-PIP qualifies for exemption under
FIFRA, i.e., that the PVCP-PIP meets
§§ 174.21(a), (b), and (c).This
certification must contain:
(i) The name of the crop (including
genus and species) containing the
PVCP-PIP.
(ii) The name of the virus from which
the coat protein gene was derived.
(iii) The name of the virus(es) to
which resistance is conferred.
(iv) When available, a unique
identifier.
5. By revising § 174.480 to read as
follows:
§ 174.480
Scope and purpose.
This subpart lists the inert ingredients
that may be used in a plant-incorporated
protectant listed in subpart B of this part
and whose residues are either exempted
from the requirement of a tolerance
under FFDCA or no tolerance would
otherwise be required.
6. By adding § 174.486 to read as
follows:
§ 174.486 Inert ingredients that may be
used with PIPs in certain plants.
The following must be used in a plant
that satisfies § 174.27(a) in order to be
exempt from the requirements of FIFRA.
(a) Beta-D-glucuronidase (GUS) from
Escherichia coli and the genetic material
necessary for its production.
(b) Neomycin phosphotransferase II
(NPTII) and the genetic material
necessary for its production.
(c) Phosphomannose isomerase (PMI)
and the genetic material necessary for
its production.
(d) CP4 enolpyruvylshikimate-3phosphate (CP4 EPSPS) and the genetic
material necessary for its production.
(e) Glyphosate oxidoreductase (GOX
or GOXv247) and the genetic material
necessary for its production.
(f) Phosphinothricin acetyltransferase
(PAT) and the genetic material
necessary for its production.
(g) Partial tetracycline resistance gene
under the control of a bacterial promoter
as present in papaya line 55–1.
[FR Doc. E7–7297 Filed 4–17–07; 8:45 am]
BILLING CODE 6560–50–S
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ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 174
[EPA–HQ–OPP–2006–0643; FRL–8100–5]
RIN 2070–AD49
Exemption from the Requirement of a
Tolerance under the Federal Food,
Drug, and Cosmetic Act for Residues
of Plant Virus Coat Proteins that are
Part of a Plant-Incorporated Protectant
(PVC-Proteins); Supplemental
Proposal
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
SUMMARY: EPA is proposing to exempt
from the Federal Food, Drug, and
Cosmetic Act (FFDCA) section 408
requirement of a tolerance, residues of
coat proteins from viruses that naturally
infect plants that humans consume
when such coat proteins are produced
in living plants as part of a plantincorporated protectant (PIP) and the
criteria proposed for this exemption are
met. EPA believes there is a reasonable
certainty that no harm will result from
aggregate exposure to such residues,
including all anticipated dietary
exposures and all other exposures for
which there is reliable information. This
proposed exemption would eliminate
the need to establish a maximum
permissible level in food for these
residues.
DATES: Comments must be received on
or before July 17, 2007.
ADDRESSES: Submit your comments,
identified by docket identification (ID)
number EPA–HQ–OPP–2006–0643, by
one of the following methods:
• Federal eRulemaking Portal: https://
www.regulations.gov. Follow the on-line
instructions for submitting comments.
• Mail: Office of Pesticide Programs
(OPP) Regulatory Public Docket (7502P),
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001.
• Delivery: OPP Regulatory Public
Docket (7502P), Environmental
Protection Agency, Rm. S–4400, One
Potomac Yard (South Bldg.), 2777 S.
Crystal Dr., Arlington, VA. Deliveries
are only accepted during the Docket’s
normal hours of operation (8:30 a.m. to
4 p.m., Monday through Friday,
excluding legal holidays). Special
arrangements should be made for
deliveries of boxed information. The
Docket Facility telephone number is
(703) 305–5805.
• Instructions: Direct your comments
to docket ID number EPA–HQ–OPP–
E:\FR\FM\18APP2.SGM
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Agencies
[Federal Register Volume 72, Number 74 (Wednesday, April 18, 2007)]
[Proposed Rules]
[Pages 19590-19640]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E7-7297]
[[Page 19589]]
-----------------------------------------------------------------------
Part II
Environmental Protection Agency
-----------------------------------------------------------------------
40 CFR Part 174
Exemption Under the Federal Insecticide, Fungicide, and Rodenticide
Act for Certain Plant-Incorporated Protectants Derived From Plant Viral
Coat Protein (PVCP-PIPs) Gene(s); Supplemental Proposal; Proposed Rules
Federal Register / Vol. 72, No. 74 / Wednesday, April 18, 2007 /
Proposed Rules
[[Page 19590]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 174
[EPA-HQ-OPP-2006-0642; FRL-8100-7]
RIN 2070-AD49
Exemption Under the Federal Insecticide, Fungicide, and
Rodenticide Act for Certain Plant-Incorporated Protectants Derived From
Plant Viral Coat Protein Gene(s) (PVCP-PIPs); Supplemental Proposal
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: EPA is proposing to exempt from Federal Insecticide,
Fungicide, and Rodenticide Act (FIFRA) requirements plant-incorporated
protectants derived from plant viral coat protein genes (PVCP-PIPs)
when the PVCP-PIP meets specified criteria. EPA is proposing this
exemption because the Agency believes that the PVCP-PIPs covered by
this exemption would be of a character which is unnecessary to be
subject to FIFRA in order to carry out the purposes of the Act.
DATES: Comments must be received on or before July 17, 2007.
ADDRESSES: Submit your comments, identified by docket identification
(ID) number EPA-HQ-OPP-2006-0642, by one of the following methods:
Federal eRulemaking Portal: https://www.regulations.gov/.
Follow the on-line instructions for submitting comments.
Mail: Office of Pesticide Programs (OPP) Regulatory Public
Docket (7502P), Environmental Protection Agency, 1200 Pennsylvania
Ave., NW., Washington, DC 20460-0001.
Delivery: OPP Regulatory Public Docket (7502P),
Environmental Protection Agency, Rm. S-4400, One Potomac Yard (South
Building), 2777 S. Crystal Drive, Arlington, VA. Deliveries are only
accepted during the Docket's normal hours of operation (8:30 a.m. to 4
p.m., Monday through Friday, excluding legal holidays). Special
arrangements should be made for deliveries of boxed information. The
Docket telephone number is (703) 305-5805.
Instructions: Direct your comments to docket ID number EPA-HQ-OPP-
2006-0642. EPA's policy is that all comments received will be included
in the docket without change and may be made available on-line at
https://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 regulations.gov or e-
mail. The Federal regulations.gov website 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 e-mail comment directly to EPA without going through
regulations.gov, your e-mail address will be automatically captured and
included as part of the comment that is placed in the 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.
Docket: All documents in the docket are listed in the docket 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, is not placed on the Internet and will be publicly available
only in hard copy form. Publicly available docket materials are
available either in the electronic docket at https://
www.regulations.gov, or, if only available in hard copy, at the OPP
Regulatory Public Docket in Rm. S-4400, One Potomac Yard (South
Building), 2777 S. Crystal Drive, Arlington, VA. The hours of operation
of this Docket Facility are from 8:30 a.m. to 4 p.m., Monday through
Friday, excluding legal holidays. The Docket telephone number is (703)
305-5805.
FOR FURTHER INFORMATION CONTACT: Melissa Kramer, Hazard Assessment
Coordination and Policy Division (7202M), Office of Science
Coordination and Policy, 1200 Pennsylvania Ave. NW, Washington, DC
20460-0001; telephone number: (202) 564-8497; fax number: (202) 564-
8502; e-mail address: kramer.melissa@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does This Notice Apply to Me?
You may be potentially affected by this action if you are a person
or company involved with agricultural biotechnology that may develop
and market plant-incorporated protectants. Potentially affected
entities may include, but are not limited to:
Pesticide and Other Agricultural Chemical Manufacturing
(NAICS code 32532), e.g., establishments primarily engaged in the
formulation and preparation of agricultural and household pest control
chemicals;
Crop Production (NAICS code 111), e.g., establishments
primarily engaged in growing crops, plants, vines, or trees and their
seeds;
Colleges, Universities, and Professional Schools (NAICS
code 611310), e.g., establishments of higher learning which are engaged
in development and marketing of virus-resistant plants;
Research and Development in the Physical, Engineering, and
Life Sciences (NAICS code 54171), e.g., establishment primarily engaged
in conducting research in the physical, engineering, or life sciences,
such as agriculture and biotechnology.
This listing is not intended to be exhaustive, but rather provides
a guide for readers regarding entities likely to be affected by this
action. Other types of entities not listed in this unit could also be
affected. The North American Industrial Classification System (NAICS)
codes have been provided to assist you and others in determining
whether this action might apply to certain entities. To determine
whether you or your business may be affected by this action, you should
carefully examine the applicability provisions in 40 CFR part 174. If
you have any questions regarding the applicability of this action to a
particular entity, consult the person listed under FOR FURTHER
INFORMATION CONTACT.
B. What Should I Consider as I Prepare My Comments for EPA?
1. Docket. EPA has established a docket for this action under
docket identification (ID) number EPA-HQ-OPP-2006-0642. Publicly
available docket materials are available either in the electronic
docket at https://www.regulations.gov, or, if only available in hard
copy, at the Office of Pesticide Programs (OPP) Regulatory Public
Docket in Rm. S-4400, One Potomac Yard (South Building), 2777 S.
Crystal Drive Arlington, VA. The hours of operation of this Docket
Facility are from 8:30 a.m. to 4 p.m., Monday through Friday, excluding
legal holidays. The Docket telephone number is (703) 305-5805.
[[Page 19591]]
2. Tips for preparing your comments. When submitting comments,
remember to:
i. Identify the document by docket ID number and other identifying
information (subject heading, Federal Register date, and page number).
ii. 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.
iii. Explain why you agree or disagree; suggest alternatives and
substitute language for your requested changes.
iv. Describe any assumptions and provide any technical information
and/or data that you used.
v. If you estimate potential costs or burdens, explain how you
arrived at your estimate in sufficient detail to allow for it to be
reproduced.
vi. Provide specific examples to illustrate your concerns and
suggest alternatives.
vii. Explain your views as clearly as possible, avoiding the use of
profanity or personal threats.
viii. Make sure to submit your comments by the comment period
deadline identified.
II. Background
A. What Action is the Agency Proposing?
EPA is proposing an exemption from FIFRA for certain plant virus
coat protein plant-incorporated protectants or ``PVCP-PIPs.'' EPA is
proposing to define a PVCP-PIP as ``a plant-incorporated protectant
derived from one or more genes that encode a coat protein of a virus
that naturally infects plants. This includes plant-incorporated
protectants derived from one or more plant viral coat protein genes
that produce only RNA and no virus-related protein.'' PVCP-PIPs
introduced into plants with the intention of preventing or mitigating
viral disease meet the FIFRA section 2(u) definition of ``pesticide''
because they are introduced into plants with the intention of
``preventing, destroying, repelling, or mitigating any pest...'' (7
U.S.C. 136(u)) and plant viruses meet the FIFRA section 2 definition of
``pest'' (7 U.S.C. 136(t)). EPA is proposing this exemption because the
Agency believes that the PVCP-PIPs covered by this exemption would be
of a character which is unnecessary to be subject to FIFRA in order to
carry out the purposes of the Act.
A PIP can be exempt from the requirements of FIFRA, other than the
adverse effects reporting requirements of 40 CFR 174.71, if it meets
all three of the requirements listed in 40 CFR 174.21. Section
174.21(a) requires that the PIP meet the criteria listed in at least
one of the sections in Sec. Sec. 174.25 through 174.50. Section
174.21(b) requires that when the PIP is intended to be produced and
used in a crop used as food, the residues of the PIP are either
exempted from the requirement of a tolerance under FFDCA or no
tolerance would otherwise be required for the PIP. Section 174.21(c)
requires that an exempt PIP must contain only those inert ingredient(s)
included on the list codified at Sec. Sec. 174.485 through 174.490.
(Reference to Sec. Sec. 174.485 through 174.490 in Sec. 174.21(c) is
proposed to be changed to refer to Sec. Sec. 174.485 through 174.486
in today's Proposed Rule.) See Unit II.F. for further discussion of
these Sec. 174.21 criteria.
The rule proposed in today's Federal Register would establish 40
CFR 174.27, which would contain three criteria that, when met, would
allow PVCP-PIPs to meet the general requirement for exemption for all
PIPs listed at 40 CFR 174.21(a). Today's Federal Register also proposes
to add several substances known to be used as inert ingredients in PIPs
to 40 CFR part 174 subpart X, thereby potentially expanding the PVCP-
PIPs that could meet the conditions of Sec. 174.21(c). A companion
document published elsewhere in today's Federal Register also proposes
a tolerance exemption for certain PVCP-PIP residues, thereby
potentially expanding the PVCP-PIPs that could meet the conditions of
Sec. 174.21(b).
The three criteria that EPA is proposing to insert at 40 CFR 174.27
are intended to address three issues that may be associated with a
PVCP-PIP. These issues are:
The potential for increased weediness or invasiveness of
the crop plant containing the PVCP-PIP or any wild or weedy relatives
that could acquire the PVCP-PIP through gene flow thereby causing
negative effects on either the agro-ecosystem or natural environments.
This issue is addressed in proposed Sec. 174.27(a).
The potential that viruses with novel properties could
develop through novel viral interactions. This issue is addressed in
proposed Sec. 174.27(b).
The potential for human or nontarget organism exposure to
proteins that have not previously existed in nature and thus should be
examined to determine whether they have potentially toxic or allergenic
properties. This issue is addressed in proposed Sec. 174.27(c).
In order to satisfy 40 CFR 174.21(a), a PVCP-PIP would have to
satisfy proposed Sec. 174.27(a), (b), and (c). The requirements at
Sec. 174.27(d) would also have to be met to qualify for exemption.
Proposed Sec. 174.27(a), (b), and (c) each can be met in one of two
ways: a product developer may self-determine that paragraph (1) of the
criterion applies (i.e., Sec. 174.27(a)(1), (b)(1), or (c)(1)) or the
Agency may determine that paragraph (2) of the criterion applies (i.e.,
Sec. 174.27(a)(2), (b)(2), or (c)(2), respectively). Paragraph (1) of
each proposed criterion (i.e., Sec. 174.27(a)(1), (b)(1), and (c)(1))
describes an objective, well-defined characteristic. Therefore, the
developer may determine whether the PVCP-PIP meets the requirement.
Paragraph (2) of each proposed criterion (i.e., Sec. 174.27(a)(2),
(b)(2), and (c)(2)) is conditioned on an Agency determination because
it may involve analysis of several types of information. Each criterion
may be satisfied either by self determination under paragraph (1) or
Agency determination under paragraph (2) irrespective of how the other
two criteria are satisfied; there is no requirement that all three
criteria must be satisfied under either paragraph (1) or paragraph (2)
in order to qualify for the exemption.
B. What is the Agency's Authority for Taking this Action?
This rule is promulgated under the authority of FIFRA sections
3(a), 25(a), and 25(b) (7 U.S.C. 136a(a), 136w(a), and 136w(b)).
FIFRA section 3(a) states that, except as provided by the Act, no
person may distribute or sell in the United States any pesticide that
is not registered under the Act (7 U.S.C. 136(a)). FIFRA section 2(u)
defines ``pesticide'' as: ``(1) any substance or mixture of substances
intended for preventing, destroying, repelling, or mitigating any pest,
(2) any substance or mixture of substances intended for use as a plant
regulator, defoliant, or desiccant, and (3) any nitrogen
stabilizer...'' (7 U.S.C. 136(u)). Under FIFRA section 2(t), the term
``pest'' includes ``(1) any insect, rodent, nematode, fungus, weed, or
(2) any other form of terrestrial or aquatic plant or animal life or
virus, bacteria, or other microorganism... which the Administrator
declares to be a pest...'' subject to certain exceptions (7 U.S.C.
136(t)).
Before EPA may register a pesticide under FIFRA, the applicant must
show that the pesticide ``when used in accordance with widespread and
commonly recognized practice... will not generally cause unreasonable
adversese effects on the environment'' (7 U.S.C. 136a(c)(5)(D)). The
term ``environment'' includes ``water, air, land, and all plants and
man and other
[[Page 19592]]
animals living therein, and the interrelationships which exist among
these'' (7 U.S.C. 136(j)). FIFRA section 2(bb) defines the term
``unreasonable adverse effects on the environment'' to mean: ``(1) any
unreasonable risk to man or the environment, taking into account the
economic, social, and environmental costs and benefits of the use of
any pesticide, or (2) a human dietary risk from residues that result
from a use of a pesticide in or on any food inconsistent with the
standard under section 408 of the Federal Food, Drug, and Cosmetic
Act'' (7 U.S.C. 136(bb)).
Although FIFRA requires the registration of most pesticides, it
also authorizes the regulation of unregistered pesticides. FIFRA
section 3(a) provides that, to the extent necessary to prevent
unreasonable adverse effects on the environment, the Administrator may
limit the distribution, sale, or use of any pesticide that is not
registered under section 3 of FIFRA, subject to an experimental use
permit under section 5 of FIFRA, or subject to an emergency exemption
under section 18 of FIFRA. Pesticides that are ``not registered''
include pesticides that are exempt from FIFRA requirements under
section 25(b).
An unregistered pesticide may be distributed or sold if it is
exempted by regulation under FIFRA section 25(b). Under FIFRA section
25(b)(2), the Agency can exempt pesticides from some or all of the
requirements of FIFRA when the Agency determines that the pesticide is
``of a character which is unnecessary to be subject to [FIFRA] in order
to carry out the purposes of this Act'' (7 U.S.C. 136w(b)(2)). EPA
interprets section 25(b)(2) to authorize the Agency to exempt a
pesticide or category of pesticides that EPA determines (1) poses a low
probability of risk to the environment and (2) is not likely to cause
unreasonable adverse effects to the environment even in the absence of
regulatory oversight under FIFRA. This standard differs from the
standard for registration which considers only whether the pesticide
``when used in accordance with widespread and commonly recognized
practice... will not generally cause unreasonable adverse effects on
the environment'' (7 U.S.C. 136a(c)(5)(D)).
In evaluating the first condition that must be met for the Agency
to exempt a pesticide, i.e., whether use of the pesticide poses a low
probability of risk to the environment, EPA considers the extent of the
potential risks caused by use of the pesticide to the environment,
including humans and other animals, plants, water, air and land.
Potential risks to humans include dietary risks as well as non-dietary
risks such as those resulting from occupational or residential exposure
to the pesticide. EPA uses the FFDCA section 408 standard in evaluating
dietary risks as discussed in Unit II.C. of this preamble. EPA will not
exempt pesticides unless they pose a low probability of risk to the
environment.
In evaluating the second condition that must be met for the Agency
to exempt a pesticide, i.e., whether the use of the pesticide is
unlikely to cause unreasonable adverse effects on the environment even
in the absence of regulatory oversight under FIFRA, EPA balances all
the potential risks to human health, including dietary risks (see Unit
II.C. of this preamble for discussion of the FFDCA standard), and risks
to the remainder of the environment from use of the pesticide against
the potential benefits associated with its use. In balancing risks and
benefits, EPA considers the economic, social, and environmental costs
and benefits of the use of the pesticide. If the pesticide poses a low
probability of risk to the environment and is not likely to cause
unreasonable adverse effects to the environment even in the absence of
regulatory oversight under FIFRA, EPA may exempt the pesticide from
regulation under FIFRA.
C. What is the Relationship of FIFRA Exemptions to the FFDCA Section
408 Standard?
Under FFDCA section 408(a), a pesticide chemical residue in or on a
food (hereafter simply ``in food'') is not considered safe unless EPA
has issued a tolerance for the residue and the residue is within the
established tolerance limit or EPA has issued an exemption from the
requirement of a tolerance for the residue (21 U.S.C. 346a(a)(1)).
FFDCA section 408 authorizes EPA to determine a residue is safe and
therefore exempt from the requirement of a tolerance if the
Administrator ``has determined that there is a reasonable certainty
that no harm will result from aggregate exposure to the pesticide
chemical residue, including all anticipated dietary exposures and all
other exposures for which there is reliable information'' (21 U.S.C.
346a(c)(2)(A)(ii)). Section 408 of the FFDCA also directs EPA to
specifically consider harm that may result to infants and children as a
result of pesticide chemical residues. For additional discussion of
this standard, see the Exemption from the Requirement of a Tolerance
under the Federal Food, Drug, and Cosmetic Act for Residues of Plant
Virus Coat Proteins that are Part of a Plant-Incorporated Protectant
published concurrently in today's Federal Register.
EPA uses the FFDCA section 408 safety standard in evaluating
whether a pesticide used in food meets the FIFRA section 25(b)(2)
exemption standard with respect to human dietary risk. A pesticide in
food poses a low probability of human dietary risk if it meets the
FFDCA section 408 standard for an exemption from the requirement of a
tolerance. Such a pesticide also is not likely to cause unreasonable
adverse effects to the environment, with respect to human dietary risk
only, if the dietary risks resulting from use of that pesticide are
consistent with the FFDCA section 408 exemption standard, and the
potential benefits of use outweigh any dietary risk even in the absence
of regulatory oversight.
FIFRA, however, does not provide for exemption of a pesticide in
food based solely upon human dietary risk and consistency with the
FFDCA section 408 exemption standard; an exemption from the
requirements of FFDCA does not exempt a product from regulation under
FIFRA. For an exemption under FIFRA, EPA must also evaluate non-dietary
risks to humans and the remainder of the environment from the pesticide
and determine both that the pesticide poses only a low probability of
non-dietary risks and that use of the pesticide is not likely to cause
any unreasonable adverse effects to the environment from such
nondietary risks in the absence of regulation.
D. What is the Role of Other Federal Agencies?
EPA is the Federal agency responsible for the regulation of
pesticides. Under the Coordinated Framework for Regulation of
Biotechnology (51 FR 23302, June 26, 1986), EPA works closely with the
U.S. Department of Agriculture (USDA), which has responsibilities under
the Plant Protection Act (PPA), and the U.S. Food and Drug
Administration (FDA), which has responsibilities under FFDCA. EPA,
USDA, and FDA consult and exchange information when such consultation
is helpful in resolving safety questions. The three agencies also
strive for consistency between programs following one of the basic
tenets of the Coordinated Framework, i.e., that the agencies composing
the Framework adopt consistent approaches to the extent permitted by
the respective statutory authorities. A consistent approach between
agencies is easier for the regulated community to understand, and it
likely conserves resources
[[Page 19593]]
because data developed for one agency may meet at least some of the
requirements posed by another agency for the same or similar products.
1. USDA. USDA has the responsibility of preventing the introduction
and dissemination of plant pests under the PPA. Before a genetically
engineered plant that is subject to the PPA may be introduced into the
environment, approval must be obtained from the USDA/Animal Plant
Health Inspection Service (APHIS) unless such a plant has been reviewed
and granted Nonregulated Status. The USDA regulations use genetic
engineering and potential plant pest risk as criteria for determining
the scope of its regulations (62 FR 23945, May 2, 1997). Any
genetically engineered plant that contains genetic material from a
plant pest is subject to the regulations. Thus, all plants containing
PVCP-PIPs are subject to USDA/APHIS requirements under the PPA.
EPA therefore recognizes that there is a potential for duplicative
oversight with respect to certain issues that may arise in decisions
about PVCP-PIPs that require any review by EPA. For example, in its
reviews of Petitions for Determination of Nonregulated Status under
regulations at 7 CFR part 340, the potential for weediness, for
displacement of native species, and potential consequences of gene
transfer are evaluated by USDA/APHIS. EPA and USDA/APHIS will continue
to consult and collaborate on reviews of PVCP-PIPs. EPA and USDA/APHIS
will work together to avoid potential duplication and inconsistencies
and to coordinate their analyses in accordance with their respective
expertise and jurisdiction.
2. FDA. FDA is the primary U.S. agency responsible for ensuring the
safety of commercial food and food additives. FDA's authority under
FFDCA extends to any nonpesticidal substance that may be introduced
into a new plant variety and that is expected to become a component of
food. Pursuant to sections 201 and 408 of FFDCA and the creation of
EPA, pesticide chemical residues are subject to EPA's regulatory
authority under FFDCA.
E. What is a PVCP-PIP?
EPA is proposing to define a PVCP-PIP as ``a plant-incorporated
protectant derived from one or more genes that encode a coat protein of
a virus that naturally infects plants. This includes plant-incorporated
protectants derived from one or more plant viral coat protein genes
that produce only RNA and no virus-related protein.''
Coat proteins are those substances that viruses produce to
encapsulate and protect the viral nucleic acid and to perform other
important tasks for the virus, e.g., assistance in viral replication,
movement within the plant, and transmission of the virus from plant to
plant by insects (Ref. 1). In many cases, when the genetic material
encoding a plant virus coat protein is engineered into a plant's
genome, the plant displays resistance to infection by that virus as
well as other viruses having similar coat protein sequences (Ref. 2).
Current scientific information suggests that prevention or
mitigation of disease by PVCP-PIPs may occur by two different
mechanisms. For some PVCP-PIPs, resistance is believed to be protein-
mediated because efficacy is correlated with the concentration of coat
protein produced by the transgene (Ref. 3). In protein-mediated
resistance, the coat protein is thought to impede the infection cycle
by interfering with the disassembly of infecting viruses (Ref. 4).
In transgenic plants, a second mechanism of resistance, post-
transcriptional gene silencing (PTGS) may be activated. In PTGS,
prevention or mitigation of viral disease is not correlated with the
level of coat protein expression. Indeed, virus resistance can occur
even when a coat protein gene expresses untranslatable RNA sequences
and no coat protein is detected (Ref. 4). PTGS is a defense mechanism
in plants against foreign RNA (e.g., viruses) in which sequence-
specific RNA degradation is initiated by the plant in response to the
foreign RNA itself. Evidence suggests that PTGS is initiated once there
is a threshold accumulation of double-stranded (ds) RNA in the cell
cytoplasm (Ref. 5). Over 90% of plant viruses have single-stranded RNA
genomes, but viral replication transiently produces dsRNA in quantities
sufficient to trigger PTGS (Ref. 6). PTGS is also known to occur with
transgenes that are transcribed at a low level but that likely produce
dsRNA (Ref. 7). Once the plant recognizes the dsRNA, it is thought to
be cleaved by a dsRNA-specific nuclease to produce small 21- to 25-
nucleotide short interfering RNA sequences (siRNAs; Ref. 8). The siRNAs
are thought to serve as guides for the cleavage of single-stranded RNA
with a sequence similar to the dsRNAs (Ref. 9). Thus once PTGS is
initiated, it targets all RNA with high sequence similarity to the
sequence that initiated the process, regardless of whether it was
transcribed from the transgene, an endogenous gene, or viral RNA.
A plant virus coat protein transgene that confers virus resistance
through either a protein- or RNA-mediated mechanism would fall within
EPA's proposed definition of a PVCP-PIP. The substances involved in
either mechanism of resistance would meet the FIFRA definition of a
pesticide because the transgene and any material expressed from the
transgene are introduced into a plant for the purpose of preventing or
mitigating viral disease (see Unit II.A.).
The proposed definition of a PVCP-PIP contains the phrase
``naturally infects plants.'' Including this phrase in the definition
would specifically limit the proposed exemption by requiring that the
virus coat protein gene sequence used in the PVCP-PIP be based
exclusively on a plant virus sequence. This limitation is proposed in
order to exclude from the definition any coat proteins of plant viruses
that have been modified with sequences from animal or human viruses.
EPA includes this concept in today's proposal in response to comment
received from the public in earlier Federal Register documents
pertaining to PVCP-PIPs.
F. What Conditions Must be Met for a PVCP-PIP to Qualify for a FIFRA
Exemption?
As noted above, a PIP is exempt from the requirements of FIFRA,
other than the adverse effects reporting requirements of 40 CFR 174.71,
if the PIP meets the requirements in 40 CFR 174.21(a), (b), and (c).
Therefore, the following factors need to be considered to determine the
FIFRA status of a PVCP-PIP. First, does the PVCP-PIP meet the
requirement at 40 CFR 174.21(a)? Second, do the residues of the PVCP-
PIP meet the requirement at 40 CFR 174.21(b)? Third, do the inert
ingredients that are part of the PVCP-PIP meet the requirement at 40
CFR 174.21(c)?
1. Does the PVCP-PIP meet the requirement at 40 CFR 174.21(a)?
Section 174.21(a) requires that the PIP meet the criteria listed in at
least one of the sections in Sec. Sec. 174.25 through 174.50. Today's
action proposes to establish Sec. 174.27, which would contain criteria
allowing certain PVCP-PIPs to meet the Sec. 174.21(a) requirement for
exemption. These criteria identify those PVCP-PIPs that EPA has been
able to determine meet the standard under FIFRA section 25(b)(2), i.e.,
that pose a low probability of risk to the environment and that are not
likely to cause unreasonable adverse effects to the environment even in
the absence of regulatory oversight under FIFRA. EPA is proposing
criteria that address the
[[Page 19594]]
relevant potential risks associated with these products:
i. The potential for increased weediness or invasiveness of the
crop plant containing the PVCP-PIP or any wild or weedy relatives that
could acquire the PVCP-PIP through gene flow thereby causing negative
effects on either the agro-ecosystem or natural environments. This
issue is addressed at Sec. 174.27(a) and is referred to as
``weediness'' for the purposes of this document.
ii. The potential for viruses with novel properties developing
through novel viral interactions. This issue is addressed at Sec.
174.27(b) and is referred to as ``viral interactions'' for the purposes
of this document.
iii. The potential for human or nontarget organism exposure to
proteins that may not have previously existed in nature and thus should
be examined to determine whether they have potentially toxic or
allergenic properties. This issue is addressed at Sec. 174.27(c) and
is referred to as ``protein production'' for the purposes of this
document.
Proposed Sec. Sec. 174.27(a), (b), and (c) are discussed in
greater detail in Unit III of this Federal Register document. In
addition, a graphical depiction of what this rule is proposing is
available in the docket for this proposed rule.
2. Do the residues of the PVCP-PIP meet the requirement at 40 CFR
174.21(b)? Section 174.21(b) requires that in order to qualify for a
FIFRA exemption, the residues of a PVCP-PIP that is intended to be
produced and used in a crop used as food must either be exempted from
the requirement of a tolerance under FFDCA or no tolerance would
otherwise be required for the PVCP-PIP. Therefore, if a PVCP-PIP is
used in a food plant (e.g., the PVCP-PIP is produced and used in a corn
plant) or residues of the PVCP-PIP might reasonably be expected in food
(e.g., the PVCP-PIP is produced and used in an ornamental plant but
could move through gene flow to a sexually compatible food plant), the
FFDCA section 408 requirements must be considered when determining
whether the PVCP-PIP can be exempted under FIFRA. If a PVCP-PIP would
not be used in and would not reasonably be expected in a crop used as
food (e.g., the PVCP-PIP is produced and used in an ornamental plant
with no sexually compatible relatives that are food plants), the FFDCA
section 408 requirements do not need to be considered.
EPA anticipates that in most cases the PVCP-PIP residues will
consist of residues of nucleic acids, residues of inert ingredients,
and residues of the plant virus coat protein portion of the PVCP-PIP
(the ``PVC-protein''). Residues of nucleic acids are exempt from the
requirement of a tolerance at 40 CFR 174.475. As of the time this
proposed rule is being issued, residues of those inert ingredients that
are exempt from the requirement of a tolerance are listed at 40 CFR
part 180 and 40 CFR part 174 subpart W. In a companion piece appearing
in today's Federal Register, EPA is proposing a tolerance exemption for
residues of certain PVC-proteins that meet specified criteria. Due to
different statutory requirements, the proposed FFDCA exemption criteria
differ from the criteria proposed in this Federal Register for 40 CFR
174.27 under FIFRA.
3. Do the inert ingredients that are part of the PVCP-PIP meet the
requirement at 40 CFR 174.21(c)? Section 174.21(c) requires that in
order for a PIP to qualify for exemption any inert ingredient contained
in the PIP must be codified at subpart X of 40 CFR part 174 - List of
Approved Inert Ingredients. Subpart X lists the inert ingredients (i)
that may be used in a plant-incorporated protectant listed in subpart B
(Exemptions) of part 174 and (ii) whose residues are either exempted
from the requirement of a tolerance under FFDCA or no tolerance would
otherwise be required. EPA is proposing to add several substances known
to be used commonly as inert ingredients in PIPs to 40 CFR part 174
subpart X. These substances already have tolerance exemptions under
FFDCA. EPA proposes in today's Federal Register that these substances,
when used in exempt PIPs as inert ingredients under specified
conditions, should also be exempt from FIFRA because they are of a
character which is unnecessary to be subject to FIFRA in order to carry
out the purposes of the Act.
G. What if a PVCP-PIP Does Not Qualify for Exemption?
If EPA is unable to conclude that a PVCP-PIP meets the standard for
exemption, an applicant may still apply to register the PVCP-PIP under
section 3 of FIFRA. EPA may be able to conclude that the PVCP-PIP meets
the standard for registration (i.e., when it is used in accordance with
widespread and commonly recognized practice, it will not generally
cause unreasonable adverse effects on the environment). EPA recognizes
that the proposed exemption criteria may not identify all low risk
PVCP-PIPs. A case-by-case review for registration would allow the
Agency to evaluate factors not readily incorporated into clear,
unambiguous exemption criteria. As part of registration, the Agency
could also impose conditions of use as appropriate. As is EPA's general
practice regarding registration of PIPs, the Agency will consult with
USDA in evaluating PVCP-PIPs for registration.
H. What is the History of this Proposal?
1. Scientific input. EPA sponsored or cosponsored with other
Federal agencies, six conferences relevant to development of this
proposed rule: on October 19-21, 1987, a meeting on ``Regulatory
Considerations: Genetically Engineered Plants'' at Cornell University
in Ithaca, New York; on September 8-9, 1988, a ``Transgenic Plant
Conference'' in Annapolis, Maryland; on November 6-7, 1990, a
conference on ``Pesticidal Transgenic Plants: Product Development, Risk
Assessment, and Data Needs'' in Annapolis, Maryland; on April 18-19,
1994, a ``Conference on Scientific Issues Related to Potential
Allergenicity in Transgenic Food Crops'' in Annapolis, Maryland; on
July 17-18, 1997, a ``Plant Pesticide Workshop'' in Washington, DC; and
on December 10-12, 2001 a conference on ``Assessment of the Allergenic
Potential of Genetically Modified Foods'' in Chapel Hill, North
Carolina. EPA incorporated information from these conferences in
development of this proposed rule as appropriate.
EPA has requested the advice of two scientific advisory bodies at
five meetings while developing its approach to plant-incorporated
protectants. On December 18, 1992, EPA convened a FIFRA Scientific
Advisory Panel (SAP) to review a draft policy on PIPs (then called
plant-pesticides) and to respond to a series of related questions posed
by the Agency dealing primarily with EPA's approach under FIFRA. On
July 13, 1993, EPA requested the advice of a Subcommittee of the EPA
Biotechnology Science Advisory Committee (BSAC) on a series of
scientific questions dealing with EPA's approach to PIPs under FFDCA.
On January 21, 1994, EPA asked for advice on the Agency's approach to
PIPs under both statutes at a joint meeting of the SAP and the BSAC. To
evaluate more recent scientific advances, EPA again brought these
issues to a FIFRA SAP meeting on October 13-14, 2004. On December 6-8,
2005, EPA convened a SAP meeting to address a series of scientific
questions related to this proposal. EPA incorporated advice from all
five meetings in development of this proposed rule as appropriate.
2. Federal Register documents. The history of this proposal
consists of the original proposed exemption from
[[Page 19595]]
FIFRA requirements that appeared in the November 23, 1994 Federal
Register (59 FR 60519); the original proposed exemption from FFDCA
tolerance requirements in the November 23, 1994 Federal Register (59 FR
60545); and several supplemental documents appearing in the May 16,
1997 Federal Register (59 FR 27149), the July 22, 1996 Federal Register
(61 FR 37891), the April 23, 1999 Federal Register (64 FR 19958), and
the July 19, 2001 Federal Register (66 FR 37772 and 37855).
i. November 23, 1994. In a document that appeared in the November
23, 1994 Federal Register (59 FR 60519) (FRL-4755-3), EPA proposed two
alternatives under FIFRA section 25(b)(2) to exempt PVCP-PIPs from
FIFRA requirements. Option 1 proposed to categorically exempt plant-
pesticides derived from coat proteins from plant viruses (now called
PVCP-PIPs). Option 2 proposed a more limited exemption covering only
those PVCP-PIPs that would have the least potential to confer selective
advantage on free-living wild relatives of the plants that could
acquire the PVCP-PIP through gene flow (discussed in detail in Unit
III.C.3.).
Elsewhere in the November 23, 1994, Federal Register (59 FR 60545)
(FRL-4755-4), EPA proposed to exempt from the FFDCA requirement of a
tolerance, residues of plant virus coat proteins produced and used in
living plants as a plant-incorporated protectant (then called a plant-
pesticide). The proposed exemption from the requirement of a tolerance
read, ``Residues of coat proteins from plant viruses, or segments of
the coat proteins, produced in living plants as plant-pesticides are
exempt from the requirement of a tolerance'' (59 FR 60547).
ii. May 16, 1997. In August of 1996, Congress enacted the Food
Quality Protection Act (FQPA), which amended FFDCA and FIFRA. On May
16, 1997, EPA published a supplemental document in the Federal Register
(62 FR 27149) (FRL-5716-6) to provide the public with an opportunity to
comment on EPA's analysis of how certain FQPA amendments to FFDCA and
FIFRA applied to the 1994 proposed exemption from the requirement of a
tolerance for residues of viral coat proteins produced in plants as
part of a PIP. (Today's Federal Register terms such entities ``PVC-
proteins.'')
In the 1997 supplemental document, EPA explained how most of the
substantive factors that the amended FFDCA requires EPA to consider in
evaluating pesticide chemical residues had been considered in the
Agency's 1994 proposed tolerance exemption. Even though the Agency may
not have used the terminology specified in the FQPA, EPA did take into
account most of the factors (e.g., toxicity and consumption patterns)
in issuing its 1994 proposal to exempt residues of PVC-proteins, or
residues of segments of such proteins, from FFDCA tolerance
requirements. EPA therefore sought comment on the requirements imposed
by FQPA that the Agency had not addressed in its 1994 proposal,
specifically:
a. EPA's conclusion that there are no substances outside of the
food supply that may have a cumulative toxic effect with residues of
PVC-proteins,
b. EPA's conclusion that there are no substances outside of the
food supply to which humans might be exposed through non-occupational
routes of exposure that are related via a common mechanism of toxicity
to residues of PVC-proteins,
c. Any available information on PVC-proteins causing estrogenic
effects,
d. EPA's rationale, described in greater detail, for concluding
that PIPs are likely to present a limited exposure of pesticidal
substances to humans in which the predominant route of exposure will be
dietary, and
e. EPA's rationale, described in greater detail, for concluding
that the Agency's analysis concerning the dietary safety of food
containing PVC-proteins applies to infants and children as well as
adults.
Because of the 1996 FQPA, EPA's final determination under FIFRA for
PVCP-PIPs in food plants could also be affected by comments on the
companion document in today's Federal Register that proposes a
tolerance exemption for certain PVCP-PIP residues.
iii. July 22, 1996. On July 22, 1996, EPA issued a supplemental
document (61 FR 37891) (FRL-5387-4) requesting comment on one aspect of
its November 23, 1994 Federal Register document: how the concept of
inert ingredient related to plant-incorporated protectants.
iv. April 23, 1999. On April 23, 1999, EPA published a supplemental
document in the Federal Register (64 FR 19958) (FRL-6077-6) soliciting
comment on whether to change the name of pesticides produced and used
in living plants.
v. July 19, 2001. In July of 2001, EPA published a package of
notices related to PIPs in the Federal Register, including a
supplemental document (66 FR 37855) (FRL-6760-4) that provided the
public with additional opportunity to comment on the FIFRA and FFDCA
exemptions for PIPs that the Agency proposed in 1994 but had not yet
finalized by 2001. EPA also requested comment on the information,
analyses, and conclusions pertaining to these PIPs (including PVCP-
PIPs) contained in the NRC report entitled ``Genetically Modified Pest-
Protected Plants: Science and Regulation'' (Ref. 10). The public was
given an opportunity to comment on a proposal to clarify the language
of the original 1994 proposals EPA was considering in response to
public comment received on the 1994 proposal. In addition, the Agency
requested additional public comment on several scientific issues. Also
in the July 19, 2001 Federal Register (66 FR 37772) (FRL-6057-7), EPA
changed the name of these pesticides from ``plant-pesticides'' to
``plant-incorporated protectants'' or ``PIPs.''
The documents and reports of the meetings described above,
including associated public comments, are available in the public
dockets established for the associated rulemakings as described in Unit
IX of this preamble.
Today's proposed rule completely supersedes these previous
proposals. EPA does not intend to respond to comments submitted on
those proposals. Thus, individuals who believe that any comments
submitted on any of the earlier proposals remain germane to today's
proposal, should submit them (or relevant portions) again during this
comment period.
III. Proposed Exemption Criteria under Sec. 174.27
A. Structure of the Proposed Exemption Criteria under Sec. 174.27
In order to satisfy the general requirement for a FIFRA exemption
listed at 40 CFR 174.21(a), EPA is proposing to add three criteria at
40 CFR 174.27. As discussed in Unit II.F.1., the three criteria that
EPA is proposing to adopt at 40 CFR 174.27 are intended to address
three issues that are associated with potential risks of PVCP-PIPs.
The PVCP-PIP would have to meet proposed Sec. Sec. 174.27(a), (b),
and (c) to satisfy 40 CFR 174.21(a). Proposed Sec. Sec. 174.27(a),
(b), and (c) each can be met in one of two ways: a product developer
may self-determine that paragraph (1) of the criterion is met (i.e.,
Sec. 174.27(a)(1), (b)(1), or (c)(1)) or the Agency may determine that
paragraph (2) of the criterion is met (i.e., Sec. 174.27(a)(2),
(b)(2), or (c)(2), respectively). Paragraph (1) of each proposed
criterion (i.e., Sec. 174.27(a)(1), (b)(1), and (c)(1)) describes an
objective, well-defined characteristic. Therefore, the developer may
determine whether the PVCP-PIP meets the requirement. Paragraph (2) of
[[Page 19596]]
each proposed criterion (i.e., Sec. 174.27(a)(2), (b)(2), and (c)(2))
is conditioned on an Agency determination because several types of
information may need to be evaluated using a weight-of-evidence
approach to determine whether the PVCP-PIP meets the requirement and is
therefore of a nature warranting exemption.
1. Exemption by self-determination. Each criterion may be satisfied
under either paragraph (1) or paragraph (2) irrespective of how the
other two criteria are satisfied; there is no requirement that all
three criteria must be satisfied under either paragraph (1) or
paragraph (2) in order for a PVCP-PIP to qualify for the exemption.
However, if a PVCP-PIP satisfies all three criteria under paragraph (1)
by developer self determination (i.e., it meets proposed Sec. Sec.
174.27(a)(1), (b)(1), and (c)(1)) and it satisfies Sec. Sec. 174.21(b)
and (c), EPA is proposing that the developer submit a notification to
the Agency of that determination and certify that the PVCP-PIP
qualifies for exemption under FIFRA, i.e., that the PVCP-PIP meets
Sec. Sec. 174.21(a), (b), and (c). In addition, EPA is proposing that
the developer maintain information adequate to support the
determination. Such records must be made available for EPA inspection
and copying or be otherwise submitted to the Agency for review upon
request for the duration of time that the PVCP-PIP is sold or
distributed. EPA is proposing that these records be kept so that EPA
could review a particular exemption determination if needed at a future
date.
EPA is proposing to require that the notifications contain:
i. The name of the crop (including genus and species) containing
the PVCP-PIP.
ii. The name of the virus from which the coat protein gene was
derived.
iii. The name of the virus(es) to which resistance is conferred.
iv. When available, a unique identifier.
EPA is proposing this notification requirement because it provides
a mechanism that allows the Agency to keep a record of all PVCP-PIPs
that may be sold or distributed. EPA expects that such a list would be
useful to developers whose products are moving in international trade
because it would enable EPA to post information on the United States
Regulatory Agencies Unified Biotechnology Website (found at https://
usbiotechreg.nbii.gov/database_pub.asp) indicating that the developer
has determined that the product satisfies the Agency's safety
requirements. Such information can facilitate acceptance by importing
countries. Absent such a posting, the field for EPA information would
be blank, and importers might question the regulatory status of the
product in the United States. In addition, EPA considers that such a
list may be useful to the Agency for ensuring enforcement and
compliance with FIFRA regulations because it will enable compliance
personnel to ascertain the exemption status of products encountered in
distribution and trade channels.
2. Exemption by Agency determination. If a PVCP-PIP does not
satisfy a particular criterion under paragraph (1) (i.e., Sec.
174.27(a)(1), (b)(1), or (c)(1)), EPA proposes that as an alternative
route to exemption, the product developer would submit data or other
information to the Agency to demonstrate that a particular PVCP-PIP
meets paragraph (2) of that criterion (i.e., it meets Sec.
174.27(a)(2), (b)(2), or (c)(2), respectively). In addition, as part of
this submission, a developer would also include a certification as to
any determination that the product meets Sec. 174.27(a)(1), (b)(1),
and/or (c)(1), as appropriate. During its review under Sec.
174.27(a)(2), (b)(2), and/or (c)(2), EPA would not review the
developer's determination that the product met any criterion under
Sec. 174.27(a)(1), (b)(1), or (c)(1).
EPA expects that in many instances developers would have most, if
not all the information that would need to be included in any exemption
submission under Sec. Sec. 174.27(a)(2), (b)(2), or (c)(2) because it
would have been gathered in the course of product development or for
submission to USDA/APHIS as part of a petition for determination for
non-regulated status. EPA will consult with USDA in evaluating whether
a PVCP-PIP meets the conditions for an Agency-determined exemption. EPA
is proposing that information supporting the submission be maintained
as records that will be available for EPA inspection as necessary for
the duration of time that the PVCP-PIP is sold or distributed.
EPA will evaluate the information contained in the submission and
publish a notice allowing the public to comment on the Agency's
determination that a product meets Sec. 174.27(a)(2), (b)(2), and/or
(c)(2), as appropriate. EPA is providing such a public comment period
because even though the public will have had the opportunity to comment
through this proposal on the appropriateness of the criteria in Sec.
174.27(a)(2), (b)(2), and (c)(2), the public would not otherwise have
an opportunity to comment on whether a particular PVCP-PIP meets these
criteria, given that these determinations depend on a case-by-case
analysis of several types of information.
The Agency plans to publish a Federal Register notice announcing
its determination that a PVCP-PIP meets Sec. 174.27(a)(2), (b)(2),
and/or (c)(2), and if no adverse comments are received during the
comment period, the Agency's decision will be considered final, and EPA
will publish no further notice. Based on its experience with EUP
notices, EPA expects that, in general, determinations that a PVCP-PIP
qualifies for exemption will be noncontroversial and generate no
adverse comments. However, in the case of adverse comments, EPA would
publish a subsequent Federal Register notice announcing its final
determination and address all public comments. EPA would prefer
criteria in Sec. 174.27(a)(2), (b)(2), and (c)(2) that would allow the
public and PVCP-PIP developers to readily predict the outcome of an
Agency review. Such criteria would reduce regulatory uncertainty in
PVCP-PIP development and decrease the time EPA would need to evaluate
the data/information necessary to make a determination that a PVCP-PIP
meets a given criterion. However, using criteria for which
determinations can be readily predicted might reduce the number of
PVCP-PIPs that would qualify for exemption. EPA tried to balance these
concerns and proposed multiple options when the Agency was unsure how
to resolve this dilemma.
However, EPA does not believe that the considerations underlying
its decisions to grant the public a further opportunity to comment on
the Agency's decision apply in cases where the Agency rejects a
submission for an exemption. Accordingly, if EPA determines that the
product fails to meet one or more of the exemption criteria, EPA will
provide notice to the applicant of its decision on the submission and
that a registration would be required for the PVCP-PIP before the PVCP-
PIP could be sold or distributed. The product developer may then submit
an application for registration to the Agency. EPA would evaluate such
PVCP-PIPs under the existing registration process and could implement
conditions of use as appropriate.
B. Key Scientific Issues Associated with the Proposed Exemption
Criteria under Sec. 174.27
Several scientific questions concerning risk issues associated with
PVCP-PIPs have been identified:
What is the potential for a PVCP-PIP to endow plants with
characteristics
[[Page 19597]]
that could disrupt the existing network of ecological relationships in
managed, semi-managed, or natural ecosystems, e.g., through gene
transfer to wild or weedy\1\ relatives? This issue is addressed at
proposed Sec. 174.27(a) and is referred to as ``weediness'' for the
purposes of this discussion.
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\1\ In the context of the phrase ``wild and weedy'' relatives/
plants used throughout this preamble, EPA considers weedy plants to
be those with the characteristics of weeds, i.e., those that are
considered undesirable, unattractive, or troublesome, especially
when growing where they are not wanted. Wild plants are those that
occur, grow, and live in a natural state and are not domesticated,
cultivated, or tamed. EPA considers a naturalized population to be
an enduring population of domesticated plants that grows in wild
(non-cultivated) areas. EPA considers a native plant population to
be one that originates in a particular region or ecosystem.
---------------------------------------------------------------------------
What is the potential for interactions between a PVCP-PIP
and an infecting virus to affect plant virus epidemiology or
pathogenicity? This issue is addressed at proposed Sec. 174.27(b) and
is referred to as ``viral interactions'' for the purposes of this
discussion.
What is the potential for exposure of humans or nontarget
organisms to PVC-proteins with novel toxic or allergenic properties?
This issue is addressed at proposed Sec. 174.27(c) and is referred to
as ``protein production'' for the purposes of this discussion.
These three questions are addressed below under the headings of
weediness, viral interactions, and protein production, respectively.
C. Weediness
1. Scientific issues. In evaluating whether a PVCP-PIP could alter
ecological relationships among plants, EPA considered two primary
issues: (1) whether the PVCP-PIP could endow a transgenic plant itself
with an increased ability to spread into natural or semi-managed
habitats and (2) whether the transfer of a PVCP-PIP from a transgenic
plant into wild or weedy relatives could endow the wild or weedy
relative with increased competitive ability and thus disrupt ecological
relationships. Gene transfer among sexually compatible plants is a
natural phenomenon that EPA does not consider to be an environmental
risk per se. Whether the transfer of a PVCP-PIP could significantly
disrupt ecological relationships in specific instances depends on all
of the following considerations: First, does the crop plant containing
the PVCP-PIP have wild relatives with which it is able to hybridize in
nature? If it does not, there can be no gene transfer. Second, if there
are sexually compatible relatives, is the gene conferring virus
resistance likely to become stable in the population? Third, is the
stable introduction of a PVCP-PIP into the plant population (i.e.,
introgression) likely to cause the population to become more weedy/
invasive or otherwise alter its competitive ability, thereby
significantly changing the population dynamics of the plant community?
The 2005 SAP concurred that these are important considerations for
PVCP-PIPs by noting that an ``important ecological risk associated with
gene flow from crop plants into their wild relatives is that the
acquisition of crop genes might substantially alter the population
dynamics of the wild plant. In particular, a transgene introgressed
from the crop relative into a wild population might allow the wild
species to persist in larger populations across a larger geographic
range, or in a wider range of habitats. Collectively these changes in
population dynamics can be considered `increased weediness'. The
probability that a particular transgene will lead to increased
weediness depends on the phenotype conferred by the transgene and on
the ecological factor(s) currently limiting the size or distribution of
the wild species. In particular, if the transgene alters plant response
to the ecological factor limiting population size, then population
dynamics may be affected. For PVCP-PIPs, the relevant consideration is
whether virus resistance (conferred by the PVCP-PIP) leads to changes
in the size or distribution of wild plant species with the PVCP-PIP''
(Ref. 11).
i. Likelihood that a crop plant containing a PVCP-PIP could itself
disrupt ecological relationships. In considering whether a PVCP-PIP
could affect the ability of a plant to spread into natural or semi-
managed habitat at the margins of cultivated fields, i.e., to form
feral or naturalized populations, the key consideration is whether
viral infection is currently limiting the ability of agricultural crops
to do so. The 2005 SAP pointed out that PVCP-PIPs ``are developed when
virus infection of a crop reduces the crop yield, suggesting that virus
infection is quite likely in naturalized populations of the crop as
well'' (Ref. 11). However, virus infection in crop plants does not
necessarily limit the spread of the crop into natural or semi-managed
areas. As the 2005 Panel also noted, ``little is known about factors
controlling population size in plant populations in general, including
those that are currently stable, as well as those that are currently
weedy or invasive'' (Ref. 11). Few published studies are available that
evaluate this question directly, perhaps due to the general rarity of
negative results in scientific literature. However, one study did find
virus infection to have little effect on an agricultural crop. Field
experiments with transgenic virus-resistant sugar beets revealed no
competitive advantage (measured as seedling emergence and biomass
production) between the transgenic and susceptible control lines (Ref.
12).
Although virus infection has been shown to negatively impact growth
and/or reproduction of some natural plant communities (discussed below
in Unit III.C.1.ii.), EPA recognizes that there is reason to question
whether the situation would be different for crop plants. The National
Research Council (NRC) noted in 1989 that most naturalized,
domesticated crops generally are unable to effectively compete with
wild species in natural ecosystems and have not been known to acquire
this ability with the type of single-gene traits commonly introduced
through genetic modification (Ref. 13). The 1989 NRC report went on to
note that plant breeders have capitalized for decades on the fact that
relatively minor genetic changes can produce plants with altered
ecological properties, but the addition of pest resistant traits has
not been known to result in increased weediness of widely used crops
(Ref. 13). A 1989 survey of the weedy characteristics of crop versus
weed species showed that weeds possess significantly more weedy
characteristics on average than do crop plants (Ref. 14). For
domesticated crops, the traits that make them useful to humans also
reduce their competitive ability in nonagricultural habitats. Crops
that have been subjected to long-term breeding (e.g., corn and
soybeans) are unlikely to possess characteristics that would allow the
plant to compete effectively outside of managed ecosystems. Domesticity
arises because intensive breeding efforts seek to eliminate many
characteristics of the crop plant that would enhance weediness (e.g.,
seed shattering, thorns, seed dormancy, and bitterness). For example,
lack of seed shattering and seed dormancy greatly reduces the ability
of an annual crop to persist without human intervention. Highly
domesticated crops such as corn are thus unlikely to survive for
multiple generations outside agricultural fields no matter what
transgenic trait they contain, including virus resistance (Ref. 15).
However, some crop species, e.g., cranberry and blackberry may have
more similarities to their wild relatives than highly domesticated
crops such as corn or soybean. As noted by the 2005
[[Page 19598]]
SAP, ``Determining whether a particular crop can naturalize and then
spread as a weedy species is difficult to ascertain from the literature
and determining the probability that a crop will be more weedy or
invasive if it contains a PVCP-PIP is even more difficult'' (Ref. 11).
Such determinations may therefore need to rely on information not
available in public literature as part of a risk assessment for a
particular plant. Plants, such as forest trees, that may grow for many
years in natural environments or in very close proximity to natural
environments present additional difficulty in evaluating and managing
risks (Ref. 16). The period of time over which such plants would
persist is significantly longer than for annual, short-lived species.
Individual plants will therefore experience a much wider range and
variety of stress conditions, enemy attacks, and climate change, making
predictions about naturalization potential with acquired virus
resistance particularly challenging.
Thus, although EPA believes that many crop species are unlikely to
disrupt ecological relationships through acquisition of a PVCP-PIP, the
available information is insufficient to support the general
conclusions that EPA would need to make for a categorical exemption of
PVCP-PIPs. EPA would need to conclude that there is a low risk that
acquisition of a PVCP-PIP would significantly affect the
competitiveness of any of the plants currently grown as crops and that
none of these crop species would significantly disrupt ecological
relationships when modified to contain a PVCP-PIP. Therefore, the
Agency believes that it is necessary to evaluate each plant species
independently to consider whether it is likely to establish weedy or
invasive populations outside of agricultural fields in the United
States and thereby potentially significantly disrupt ecological
relationships if it becomes virus resistant due to a PVCP-PIP. Factors
likely to influence this determination cannot be readily distilled into
a straightforward criterion suitable for a categorical exemption.
ii. Likelihood that a crop plant containing a PVCP-PIP could
significantly disrupt ecological relationships through gene transfer.
The question of whether gene transfer from a crop to a wild or weedy
relative could significantly disrupt ecological relationships is a more
complicated question because a much broader range of potential plants
may be involved when wild or weedy relatives are considered in addition
to the crops themselves. The answer to this question depends first on
the question of whether the transgenic crop plants could transfer a
PVCP-PIP to other plant populations. This potential for transfer
depends in part on the frequency of hybridization between domesticated
species and their wild relatives. Hybridization is affected by the
ability of plants to cross-pollinate which in turn is affected by their
timing of reproductive viability and the proximity of the plants.
Hybridization is also affected by the ability of pollen to fertilize
recipient plants, the recipient plants to develop viable seeds, these
seeds to germinate, and the seedlings to grow into viable adults (Ref.
17). In spite of these potential constraints, a survey of the world's
most important crops suggests that spontaneous hybridization of
domesticated plants with wild relatives appears to be a general feature
across at least a portion of the worldwide geographic area over which
each is cultivated (Refs. 18 and 19). The ability to cross crops with
wild relatives (which may not necessarily occur where the crop is
grown) is also the basis of many traditional breeding techniques that
are used for virtually all crops (Ref. 20).
Whether virus infection limits the growth and/or reproductive
ability of wild or weedy plant populations is more diffic