Pesticides; Data Requirements for Biochemical and Microbial Pesticides, 12072-12117 [06-2185]
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Federal Register / Vol. 71, No. 45 / Wednesday, March 8, 2006 / Proposed Rule
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 158 and 172
[EPA–HQ–OPP–2004–0415; FRL–7763–4]
RIN 2070–AD51
Pesticides; Data Requirements for
Biochemical and Microbial Pesticides
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
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AGENCY:
SUMMARY: EPA is proposing to update
and revise its data requirements for the
registration of microbial and
biochemical pesticide products to
reflect current scientific knowledge.
These proposed revisions are intended
to provide EPA with data and other
information necessary to support the
registration of a biochemical and
microbial pesticide product, and will
improve the Agency’s ability to make
regulatory decisions about the human
health and environmental effects of
these pesticide products. EPA is also
proposing to update the definitions of a
biochemical pesticide and a microbial
pesticide to more accurately describe
these categories of pesticides, and to
make a conforming change to the
definition of microbial pesticide. EPA is
announcing its policy to provide
assistance to applicants when needed in
determining what data are appropriate
to support registration of a biochemical
or microbial pesticide and encouraging
applicants to request pre-submission
meetings to discuss these data issues.
EPA is announcing its intent to provide
assistance to applicants in some narrow
circumstances in preparation of an
applicant’s data waiver.
DATES: Comments must be received on
or before June 6, 2006.
ADDRESSES: Submit your comments,
identified by docket identification (ID)
number EPA–HQ–OPP–2004–0415, by
one of the following methods:
Federal eRulemaking Portal:https://
www.regulations.gov. Follow the on-line
instructions for submitting comments.
Mail: Public Information and Records
Integrity Branch (PIRIB) (7502C), Office
of Pesticide Programs (OPP),
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001. In addition, please mail
a copy of your comments on the
information collection provisions to the
Office of Information and Regulatory
Affairs, Office of Management and
Budget (OMB), Attn: Desk Officer for
EPA, 725 17th St. NW., Washington, DC
20503.
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Hand Delivery: Public Information
and Records Integrity Branch (PIRIB),
Office of Pesticide Programs (OPP),
Environmental Protection Agency, Rm.
119, Crystal Mall #2, 1801 S. Bell St.,
Arlington, VA. Such deliveries are only
accepted during the Docket’s normal
hours of operation, and special
arrangements should be made for
deliveries of boxed information.
Instructions: Direct your comments to
Docket ID No. EPA–HQ–OPP–2006–
0415. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at https://
www.regulations.gov/, including any
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 email. The 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 public docket and made available on
the Internet. If you submit an electronic
comment, EPA recommends that you
include your name and other contact
information in the body of your
comment and with any disk or CD-ROM
you submit. If EPA cannot read your
comment due to technical difficulties
and cannot contact you for clarification,
EPA may not be able to consider your
comment. Electronic files should avoid
the use of special characters, any form
of encryption, and be free of any defects
or viruses. For additional information
about EPA’s public docket visit the EPA
Docket Center homepage athttps://
www.epa.gov/epahome/dockets.htm.
Docket: All documents in the docket
are listed in the regulations.gov index.
Although listed in the index, some
information is not publicly available,
e.g., CBI or other information whose
disclosure is restricted by statute.
Certain other material, such as
copyrighted material, will be publicly
available only in hard copy. Publicly
available docket materials are available
either electronically in https://
www.regulations.gov or in hard copy at
the Public Information and Records
Integrity Branch (PIRIB) (7502C), Office
of Pesticide Programs (OPP),
Environmental Protection Agency, Rm.
119, Crystal Mall #2, 1801 S. Bell St.,
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Arlington, VA. This Docket Facility is
open 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:
Candace Brassard or Nathanael Martin,
U.S. Environmental Protection Agency
(7506C), 1200 Pennsylvania Ave. NW.,
Washington, DC 20460, telephone: 703–
305–6598 or 703–305–6475, e-mail:
brassard.candace@epa.gov or
martin.nathanael@epa.gov. Do not email your comments to these contacts.
Submit your comments according to the
instructions under ADDRESSES.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this Action Apply to Me?
You may be affected by this notice if
you are a producer or registrant of a
biochemical or microbial pesticide
product. This proposal also may affect
any person or company who might
petition the Agency for new tolerances
for biochemical or microbial pesticides,
or hold a pesticide registration with
existing tolerances, or any person or
company who is interested in obtaining
or retaining a tolerance in the absence
of a registration, that is, an import
tolerance for biochemical or microbial
pesticides. The following is intended as
a guide to entities likely to be regulated
by this action. The North American
Industrial Classification System
(NAICS) codes are provided to assist
you in determining whether or not this
action applies to you. Potentially
affected entities may include, but are
not limited to:
• Chemical Producers (NAICS 32532),
e.g., pesticide manufacturers or
formulators of pesticide products,
importers or any person or company
who seeks to register a pesticide or to
obtain a tolerance for a pesticide.
• Crop Production (NAICS 111).
• Animal Production (NAICS 112).
• Food Manufacturing and Processing
(NAICS 311).
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 could also be affected.
If you have questions regarding the
applicability of this action to a
particular entity, please consult the
appropriate Branch Chief in the U.S.
EPA Biopesticides and Pollution
Prevention Division of the Office of
Pesticide Programs at 703–308–8712,
fax number at 703–308–7026 or visit the
following website: https://www.epa.gov/
pesticides/biopesticides/.
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II. Overview of EPA’s Proposal
Since the data requirements were first
codified in 1984, information needed to
support the registration of a biochemical
and microbial pesticide has evolved as
the general scientific understanding of
the potential hazards posed by
pesticides has grown. Since 1984, EPA
has developed new and revised data
requirements with public participation,
extensive involvement by the scientific
community, and review by the
Scientific Advisory Panel (SAP) under
Federal Insecticide, Fungicide, and
Rodenticide Act (FIFRA), which have
been imposed on a case-by-case basis.
By codifying these data requirements,
the pesticide industry, along with other
partners in the regulated community,
will have a better understanding of and
could better prepare for the registration
process for biochemical and microbial
pesticides. In addition, the Agency is
proposing certain new data
requirements in response to the need for
strengthened risk assessment mandated
by the Food Quality Protection Act
(FQPA) and FIFRA.
EPA is also proposing to update the
definitions of a biochemical pesticide
and a microbial pesticide to more
accurately describe these categories of
pesticides, and to make a conforming
change to the definition of microbial
pesticide in 40 CFR part 172. EPA is
announcing its policy to provide
assistance to applicants when needed in
determining what data are appropriate
to support registration of a biochemical
or microbial pesticide and encouraging
applicants to request pre-submission
meetings to discuss these data issues.
EPA is announcing its intent to provide
assistance to applicants in some narrow
circumstances in preparation of an
applicant’s data waiver.
This proposed rule is one in a series
of proposals to update and clarify
pesticide data requirements. EPA
proposed data requirements for
conventional pesticides (70 FR 12276,
March 11, 2005) and is developing data
requirements specific to antimicrobial
pesticides. In the future, EPA expects to
develop data requirements for plantincorporated protectants.
EPA is proposing to update and revise
its data requirements for the registration
of microbial and biochemical pesticide
products to reflect current scientific
knowledge. These proposed revisions
are intended to provide EPA with data
and other information necessary to
support the registration of a biochemical
and microbial pesticide product, and
will improve the Agency’s ability to
make regulatory decisions about the
human health and environmental effects
of these pesticide products.
III. Statutory Authorities and
Regulatory Framework
EPA is authorized to regulate
pesticides under two Federal statutes.
FIFRA regulates the sale, distribution,
and use of pesticide products through a
licensing (registration) scheme. The
Federal Food, Drug, and Cosmetic Act
(FFDCA), among other things, regulates
the safety of pesticide residues in food
and feed. Both FIFRA and FFDCA were
amended in 1996 by the FQPA to
strengthen the protections offered, with
B. What Should I Consider as I Prepare
My Comments for EPA?
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1. Submitting CBI. Do not submit this
information to EPA through
www.regulations.gov or e-mail. Clearly
mark the part or all of the information
that you claim to be CBI. For CBI
information in a disk or CD ROM that
you mail to EPA, mark the outside of the
disk or CD ROM as CBI and then
identify electronically within the disk or
CD ROM the specific information that is
claimed as CBI). In addition to one
complete version of the comment that
includes information claimed as CBI, a
copy of the comment that does not
contain the information claimed as CBI
must be submitted for inclusion in the
public docket. Information so marked
will not be disclosed except in
accordance with procedures set forth in
40 CFR part 2.
2. Tips for preparing your comments.
When submitting comments, remember
to:
i. Identify the document by docket
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.
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particular emphasis on protection of
children.
This action is issued under the
authority of sections 3, 4, 5, 12, and 25
of FIFRA (7 U.S.C. 136–136y) and
section 408 of FFDCA (21 U.S.C. 346a).
The data required for a registration,
reregistration, experimental use permit,
or tolerance are listed in 40 CFR part
158.
A. FIFRA
In general, under FIFRA, every
pesticide product must be registered (or
specifically exempted from registration
under FIFRA section 25(b)) with EPA
before it may be sold or distributed in
the United States. To obtain a
registration, an applicant or registrant
must demonstrate to the Agency’s
satisfaction that, among other things, the
pesticide product, when used in
accordance with widespread and
commonly recognized practice, will not
cause ‘‘unreasonable adverse effects’’ to
humans or the environment. This
determination, as defined in the statute,
requires the Agency to consider the
risks and benefits associated with the
use of a pesticide. EPA must determine
that the safety standard contained in
FIFRA is met before granting a Federal
pesticide registration.
1. Registration. Section 3 of FIFRA
contains the requirements for
registration. Specifically, FIFRA sec.
3(c)(2) provides EPA broad authority,
before and after registration, to require
scientific testing and submission of the
resulting data to the Agency by
registrants and applicants of pesticide
products. An applicant for registration
must furnish EPA with substantial
amounts of data on the pesticide, its
composition, toxicity, potential human
exposure, environmental fate properties,
ecological effects, as well as information
on its efficacy in certain cases. Although
the data requirements are imposed
primarily as a part of initial registration,
EPA is authorized under FIFRA sec.
3(c)(2)(B) to require a registrant to
develop and submit additional data to
maintain a registration. Thispostregistration data call-in authority
recognizes that the scientific
underpinnings of risk assessment
change, and is another means by which
EPA may keep data for use in risk
assessment current with the evolving
science.
2. Reregistration. FIFRA sec. 4
requires that EPA reregister each
pesticide product first registered before
November 1984. This date was chosen
based upon the fact that pesticides
registered since 1984 were subject to the
40 CFR part 158 requirements of the
1984 regulations. Additional data for
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older pesticides were called in where
gaps in the scientific data base occurred.
The Agency has used its data call-in
authority to require on a case-by-case
basis the submission of most of the data
requirements contained in this proposal.
3. Experimental use permits. Subject
to some exemptions, FIFRA sec. 5
requires persons seeking experimental
use of pesticides under field conditions
to obtain an experimental use permit
(EUP). An EUP allows limited
distribution and use of a pesticide for
specified experimental and data
collection purposes intended to support
future registration of the pesticide.
Because an EUP is for limited use under
controlled conditions, the data needed
to support issuance of the permit are
correspondingly less than those
required for full registration. For
example, when performing crop field
trials, a registrant may opt to destroy the
treated crop rather than generate the
needed residue chemistry data to
establish a temporary tolerance. The
regulations governing the issuance of
EUPs are found in 40 CFR part 172.
B. FFDCA
FFDCA mandates EPA to determine
that the level of pesticide chemical
residues in food and feed will be safe for
human consumption. An applicant must
petition the Agency for a tolerance
(maximum residue level) for a pesticide
that is to be used in or around food or
feed commodities, or could otherwise
come in contact with food or feed. The
safety standard set under FFDCA sec.
408(b) and (c) defines safe as ‘‘a
reasonable certainty that no harm’’ will
result from exposures to pesticide
chemical residues. In making this
determination, EPA is directed to assess
multiple sources of pesticide exposure,
including anticipated food, drinking
water, and other non-occupational
exposures for which there is reliable
information. Under FFDCA sec.
408(b)(2)(C), EPA must make a separate
finding of safety for infants and
children. In addition, EPA must take
into account a variety of other factors,
enumerated in sec. 408(b)(2)(D),
including the cumulative risks
associated with pesticides having a
common mechanism of toxicity. The
combination of aggregate exposure and
cumulative risk increases the nature and
scope of EPA’s risk assessment, and
potentially the types and amounts of
data needed to determine that the
FFDCA safety standard is met.
1. Establishing tolerances. Under
FFDCA sec. 408, EPA is authorized to
establish tolerances for pesticide
residues in food and feed, or to exempt
a pesticide from the requirement of a
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tolerance, if warranted. As previously
mentioned, in 1996, the FQPA modified
the FFDCA to establish a single healthbased standard for tolerance-setting and
enhanced the risk assessment process to
more clearly focus on pesticide risks to
children. (In this preamble, references to
tolerances include exemptions from
tolerance since the standards and
procedures for both are essentially the
same.) The new safety standard applies
to tolerances in a number of regulatory
situations, including:
• Permanent tolerances that support
registration under FIFRA;
• Tolerances for imported products
are established to allow importation of
pesticide-treated commodities, but for
which no U.S. registration is sought;
• Time-limited tolerances which are
established for FIFRA sec. 18 emergency
exemptions; and
• Temporary tolerances established
for experimental use permits under
FIFRA sec. 5.
2. Reassessing tolerances. Under
FFDCA sec. 408(q), EPA must reassess
each tolerance established before
August 3, 1996, on a prescheduled 10–
year schedule. The Agency has
reassessed many tolerances under its
reregistration program. Numerous
regulatory decisions have been made
based upon available data and
information required by the existing
data requirements, and supplemented
by additional data provided by
registrants through data call-ins or
voluntary submissions.
C. Linking FIFRA and FFDCA Safety
Standards
Unless EPA is able to establish or
maintain a needed tolerance or
exemption under FFDCA, a pesticide
cannot be registered under FIFRA for a
food/feed use. FQPA created a specific
linkage (FIFRA sec. 2(bb)) between the
‘‘unreasonable adverse effects’’ finding
under FIFRA and the determination of
pesticide residue safety of ‘‘reasonable
certainty of no harm’’ under FFDCA. In
essence, a pesticide that is inconsistent
with, or does not meet, the FFDCA sec.
408 safety standard poses an
unreasonable adverse effect that
precludes new or continued registration.
Thus, both FIFRA and FFDCA standards
must be met for pesticides to be
registered in the United States for food
or feed uses.
Given this linkage between
registration and tolerances, it makes
sense for EPA to define data
requirements for both purposes: the data
required to support a determination of
‘‘reasonable certainty of no harm’’ under
FFDCA are an integral part of the data
needed for an ‘‘unreasonable adverse
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effects’’ determination under FIFRA.
Consequently, when promulgated, these
proposed data requirements will
encompass the basic data requirements
for both registration and tolerancesetting determinations. EPA will retain
its authority to require additional data
on a case-by-case basis.
IV. Background
A. What is the Context for Today’s
Proposal?
Under FIFRA, as previously stated,
every pesticide product must be
registered (or specifically exempted
from registration under FIFRA section
25(b)) with EPA before it may be sold
or distributed in the United States. To
obtain a registration, an applicant or
registrant must demonstrate to the
Agency’s satisfaction that, among other
things, the pesticide product, when
used in accordance with widespread
and commonly recognized practice, will
not cause ‘‘unreasonable adverse
effects’’ to humans or the environment.
This safety determination, as defined in
the statute, requires the Agency to
consider the risk of the use of the
pesticide and weigh this against its
benefit. EPA must determine that the
safety standard contained in FIFRA is
met before granting a Federal
registration. The establishment of
tolerances, if appropriate, is part of the
registration process.
B. Why does EPA Require Data for
Pesticide Registrations?
Under the FFDCA and the FIFRA,
anyone seeking to register a pesticide
product is required to provide
information to EPA that demonstrates
the product can be used without posing
unreasonable risk to human health and
the environment, and for food uses, that
there is a reasonable certainty that no
harm will result from exposures to the
residues of the pesticide product. As
appropriate for the particular pesticide
product, EPA uses the information
provided to evaluate the pesticide for a
wide range of adverse human health
effects, from eye and skin irritation to
cancer and birth defects, and to assess
how the pesticide affects animal and
plant species, nontarget insect species
and to determine what happens to the
pesticide in soil, water, and air.
C. What are the Data Requirements?
First promulgated in 1984, the data
requirements in 40 CFR part 158 (49 FR
42856, October 24, 1984) outline the
kinds of data and related information
typically needed to register a pesticide.
The data requirements are organized by
major pesticide type (e.g., conventional,
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biochemical, microbial, etc.), scientific
discipline (e.g., toxicology, etc.), and
major use sites (e.g., outdoor vs. indoor,
terrestrial, aquatic, greenhouse). Part
158 also outlines the associated
procedures for submitting the data,
requesting a waiver from a
requirement(s), and other associated
procedures. Since there is much variety
in pesticide chemistry, exposure, and
hazard, part 158 is designed to be
flexible. Table notes (referred to as test
notes) to each data requirement explain
under what conditions data are typically
needed. The Agency also recognizes,
however, that due to the particular
nature and risk of some pesticides,
registrants may seek to obtain data
waivers or may suggest alternative
approaches to satisfying requirements.
In essence, the data requirements
identify the questions that the registrant
will need to answer regarding the safety
of a pesticide product before the Agency
can register it. Data requirements
address both components of a risk
assessment, i.e., what hazards do the
pesticide present, and estimated level of
exposure to humans or nontarget
species. The answer to one question
may inform the kind of information
needed in others. For example, a
pesticide that is persistent and
toxicologically potent may require more
extensive exposure data to help
establish a safe level of exposure. If
there is negligible exposure then
extensive hazard data may not be
required since any conceivable risk
would be low.
1. The establishment of standardized
data requirements. Until 1984, data
requirements were based on
longstanding requirements initially put
in place when pesticides were regulated
by the U.S. Department of Agriculture
(USDA) and the Food and Drug
Administration (FDA). However,
because virtually all EPA decisions
relating to the registration of pesticides
or the establishment of tolerances
depend on Agency evaluation of
scientific studies, EPA has throughout
the years developed standardized data
requirements and test guidelines, and
established evaluation procedures and
peer review processes to ensure the
quality and consistency of scientific
studies.
The current provisions in part 158
were originally promulgated in October
1984. Prior to this, data requirements for
the registration of pesticides were
contained in a variety of guidance
documents, not in regulatory form. Part
158 was intended to be a concise
presentation of what data were required
and under what circumstances. Once
codified, part 158 specified standard
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hazard and exposure studies required
for registration and tolerance setting and
also identified conditions under which
more specialized studies might be
required. Guidelines, i.e., instructions
and test methods on how to perform a
study, had meanwhile been issued as a
series of Pesticide Assessment
Guidelines. These documents, updated
in 1996, describe acceptable protocols,
test conditions, and data reporting
guidelines to ensure that EPA’s
regulatory decisions are based on sound
scientific data.
2. Relationship between the
harmonized test guidelines and part 158
requirements. EPA has established a
unified library for test guidelines issued
by the Office of Prevention, Pesticides,
and Toxic Substances (OPPTS) for use
in testing chemical substances to
develop data for submission to EPA
under the Toxic Substances Control Act
(TSCA), FFDCA, or FIFRA. This unified
library of test guidelines represents an
Agency effort that began in 1991 to
harmonize the test guidelines within
OPPTS, as well as to harmonize the
OPPTS test guidelines with those of the
Organization for Economic Cooperation
and Development (OECD), which
includes representation of countries
throughout the world (including the
United States). The process for
developing and amending the test
guidelines included several
opportunities for public participation
and the extensive involvement of the
scientific community, including peer
review by the FIFRA SAP and the
Science Advisory Board (SAB) and
other expert scientific organizations.
The purpose for harmonizing these
guidelines into a single set of OPPTS
guidelines is to minimize variations
among the testing procedures that must
be performed to meet the Agency’s data
requirements under FIFRA and TSCA.
The guidelines themselves do not
impose mandatory requirements.
Instead, they provide recognized
standards for conducting acceptable
tests, guidance on reporting data,
definition of terms, consistent with the
purpose of the data requirement and the
test standard and recommended study
protocols. As such, pesticide registrants
may also use a nonguideline protocol to
generate the data required by part 158.
Typically the registrant will use the
available guideline, in which case the
study protocol would simply cite the
relevant guideline. If the registrant
deviates from these guidelines, or is
asked to provide data where there isn’t
yet a final guideline available, the
registrant is expected to fully justify the
methods chosen in the study protocol.
Nonguideline protocols may be
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accepted, provided that the study
protocol meets the purpose of the data
requirement and provides data of
suitable quality and completeness as
typified by the protocols cited in the
guidelines. More information about the
unified library and these guidelines is
available a https://www.epa.gov/
opptsfrs/home/guidelin.htm. Please see
the docket for the complete crosswalk
for old guideline numbers to new
guideline numbers (Ref. 2).
D. Why have EPA’s Data Needs Changed
Since 1984?
1. 1988 FIFRA amendments. In 1988,
FIFRA was amended to ensure that
older pesticides met the scientific
standards of the day. Among other
things, the amendments provided for
the acceleration of the reregistration
program by establishing statutory
deadlines and new procedures. During
the registration process, EPA recognized
that some of the 1984 data requirements
were becoming out of date. The Agency
then called in additional information in
order to complete the registration
process.
2. The National Academy of Sciences
1993 Report. With increasing emphasis
on protecting children’s health, EPA
began to examine its data requirements
relative to evaluating the potential risks
from pesticides to sensitive
subpopulations. The Agency sought the
advice of the National Academy of
Sciences’ National Research Council
(NRC) to assess its risk assessment
methodologies and to provide
additional information on the extent to
which children may be at risk given
emerging scientific information and
technologies. In their 1993 report
entitled, ‘‘Pesticides in the Diets of
Infants and Children,’’ NRC offered
recommendations for further protecting
infants and children from pesticides in
their diet. The NRC called for the
Agency to require more data and adopt
better risk assessment methodologies.
For example, the Council called for
increased testing in the area of immune
function and reproductive testing
(National Research Council, 1993, pp.
152–156) (Ref. 3), which applies to
biochemical and microbial pesticides.
NRC also suggested adding a thyroid
screen to existing subchronic and
chronic toxicity tests and additional
tests of age-related physiological
changes and pharmacokinetics in
immature animals. At the time the 1993
report was released, EPA had already
begun work on many of the
recommendations to improve the
quality of its risk assessments. New
testing guidelines and protocols were
developed. Since then, many of the
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testing requirements recommended by
the NRC have been incorporated into
the Agency’s standard evaluation
requirements and practices.
3. Scientific Advisory Panel Review of
1994. The FIFRA SAP completed a
review of a set of scientific issues
regarding the Environmental Protection
Agency’s Proposed Rule: Pesticide
Registration Data Requirements, 40 CFR
part 158 (Ref. 4). The Panel commended
the Agency for presenting this
regulation in such a clear and
understandable manner, and generally
endorsed the revisions. The Panel
addressed individual scientific issues
where necessary for both biochemicals
and microbial pesticides and the data
needed to address risk.
4. The Food Quality Protection Act of
1996 (FQPA). Passage of FQPA in 1996
reformed the nation’s pesticide and food
safety laws, resulting in changes in
EPA’s approach to protecting human
health from risks associated with
pesticide use. As mentioned, FQPA
modified both FIFRA and FFDCA and
established a single health-based
standard for food-use pesticides and
added protections for infants and
children. Since the early 1990s, EPA has
been continually working on improving
data requirements. Under FFDCA, as
amended by FQPA, EPA must reassess
all existing pesticide tolerances and
exemptions against the expanded and
more rigorous safety standard.
Beginning in 1994, and increasingly
since the enactment of FQPA, EPA has
changed aspects of its data requirements
and risk assessment process to improve
its ability to assess exposure more
accurately and to strengthen its
understanding of the potential pesticide
risk to children. As mentioned, risk
assessments must now consider data
relating to aggregate exposure (exposure
to pesticides from food, drinking water,
and nonoccupational routes such as
home and garden uses) and cumulative
risk (effects from exposures to multiple
pesticides that share a common
mechanism of toxicity). These measures
necessitate collection of additional data
on drinking water and nonoccupational
and residential exposure.
5. Pesticide reregistration.
Recognizing that pesticides registered in
the past may not meet today’s safety
standards, EPA is reviewing and
reregistering older pesticides and taking
action to reduce risks where
appropriate. On July 13, 2005, EPA
published a notice of proposed
rulemaking (NPRM) to establish
procedural regulations for conducting
registration review (70 FR 40251, July
13, 2005), as required in FIFRA section
3(g). Registration review will replace
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EPA’s one-time pesticide reregistration
and tolerance reassessment programs
starting in 2006. The Agency will
conduct a review of each pesticide at
least every 15 years to ensure that
registrations continue to meet statutory
standards for registration. EPA plans to
make decisions on almost 50
registration review cases, or about 80
active ingredients, each year. Under the
reregistration process required by FIFRA
section 4, EPA has been reviewing older
pesticides (those initially registered
before November 1, 1984) to consider
their health and environmental effects
and to make decisions about their future
use. EPA is committed to completing
the reregistration process by the end of
fiscal 2008.
V. Scope, Purpose, and Request for
Comments on this Proposal
A. General Background on the Phased
Rulemaking Approach
EPA is responsible for registration of
the following categories of pesticides:
Biochemicals, microbials and plantincorporated protectants, conventional
pesticides, and antimicrobial pesticides.
The various processes include differing
data requirements that registrants must
take into account in their submittals.
On March 11, 2005, EPA published a
proposed rule to update and revise its
data requirements for the registration of
conventional pesticides (70 FR 12276)
(Ref. 5). In addition to proposing
specific changes to the data
requirements for registration of
conventional pesticides, EPA proposed
a number of other changes to the general
provisions of part 158. Specifically,
subpart A of the proposed rule for
conventional chemicals describes
general provisions including
definitions, format of data submissions,
policies on Confidential Business
Information (CBI), flagging criteria,
waivers, and minor uses. Subpart B of
the proposed rule for conventional
chemicals describes expanded use
patterns, clarifications on using the data
tables, identifying data for Experimental
Use Permits (EUPs), test guidelines, and
purpose of the registration data
requirements. That proposed rule also
proposed to upgrade the structure of
part 158, assigning biochemical data
requirements to subpart L, and
microbial pesticide data requirements to
subpart M of part 158.
Today’s proposed rule proposes to
update and revise the data requirements
for the registration of biochemical and
microbial pesticides, and to maintain
the structure proposed in the earlier
proposed rule for conventional
pesticides, by placing the proposed data
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requirements for biochemical and
microbials in new subparts L and M,
respectively. When the proposed rule
for conventional pesticides is finalized,
the general provisions of subparts A and
B of that rule will apply to the other
data specific subparts, such as subparts
L and M as proposed today, unless
otherwise specified. Future rulemakings
will address the data requirements for
antimicrobials and plant-incorporated
protectants.
B. Summary of this Proposal
EPA is proposing a number of changes
to the current data tables. The proposed
rule would:
1. Codify current data requirements
that do not appear in part 158, but
which are routinely required.
2. Add new data requirements.
3. Revise certain existing data
requirements, such as by updating test
notes.
4. Clarify the definitions of both
‘‘biochemical pesticide’’ and ‘‘microbial
pesticide’’ to reflect our current
application of those terms, and make a
conforming change in the part 172
definition of ‘‘microbial pesticide.’’
5. Add additional definitions needed
to apply the data requirements properly.
6. Make necessary reorganizing and
formatting revisions, such as renaming
data requirements.
EPA will retain its current tiering
system for both biochemical and
microbial pesticide data requirements.
C. What are the Purposes of this
Proposal?
EPA has a number of objectives in
proposing this regulation to update and
revise the data requirements in 40 CFR
part 158.
1. Ensuring high quality data to meet
EPA’s mandates. Although most of the
specific requirements in part 158 have
not changed since the data requirements
were first published in 1984, aspects of
the requirements may be out of date or
may be unclear because the underlying
science has advanced (e.g., National
Academy of Sciences (NAS) in 1993
suggested changes to better protect
children) or the Agency’s legislative
mandate has been broadened to address
new concerns. For example, given the
stricter mandates imposed by the 1988
FIFRA amendments and the 1996 FQPA
amendments to FIFRA and FFDCA
(emphasis on exposure to population
subgroups), EPA finds that it is more
frequently requesting certain data, and
the Agency believes it should detail
more specifically the conditions under
which these tests will be required.
In light of this background, the
primary purpose of this proposal is to
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transparently identify the data EPA
needs and will require to support a
determination of ‘‘reasonable certainty
of no harm’’ under FFDCA and
‘‘unreasonable adverse effects’’
determination under FIFRA. In
developing this proposed rule, EPA has
evaluated its data needs to conduct the
expanded risk assessments required by
new statutory mandates. Thus, the
proposed changes entail both new tests
and broadened requirements for some
current tests, reflecting the changes in
data requirement practices that have
evolved since the 1984 data requirement
rule was promulgated and addressing
data needed to meet requirements
created by statutory amendments to
FIFRA and FFDCA.
2. Ensuring a sound scientific basis
that is consistent with advances in
scientific understanding and works
toward harmonization to avoid
duplicative data. Relatedly, these
proposed revisions are intended to
ensure that the data requirements in
part 158 reflect current scientific
understanding and scientific advances
since the data requirements were first
issued in 1984. As discussed throughout
this document, these proposed revisions
have been presented to, and reflect the
advice and recommendations of, the
NAS and FIFRA SAP. Issues and related
materials that are brought by EPA to the
FIFRA SAP undergo a public review
and comment opportunity before the
FIFRA SAP issues its report with
recommendations to the Agency.
To the extent feasible, the proposed
revisions are a reflection of the scientific
advances within OECD countries. The
United States participates in OECD
activities to harmonize international
testing standards and, where
appropriate, reference to the OECD
testing standards have been included in
this proposal. However, since EPA
continues to allow applicants to submit
and use their own study protocols
consistent with the purpose of the
requirement to generate data that they
subsequently submit to EPA, and there
are differences in the mandate and
authorities between EPA and the
governing authorities within OECD
countries, the data submitted to EPA
under part 158 would be expected to
satisfy OECD testing standards under
most circumstances for microbial testing
(because OECD has agreed to use the
U.S. microbial pesticide testing
guidelines) and for a number of
countries some of the U.S. biochemical
testing guidelines would be satisfied. A
few of the governing authorities within
the OECD countries may want
additional studies that would not
normally be required in the United
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States, but protocols for these studies
are generally acceptable to all countries.
3. Improving the depth and
transparency of the scientific basis for
pesticide registration decisions. In
general, the information developed as a
result of the revisions, if finalized as
proposed today, is expected to improve
the depth and transparency of the
Agency’s understanding of the health
and environmental effects of pesticides
to which individuals and the
environment may be exposed. For
example, the proposed rule includes a
test note for the human health
assessment data requirements indicating
data are not required to support straight
chain lepidopteran pheromones when
used at certain application rates. In
addition, EPA is proposing to continue
using the tiered testing system, as given
in the current §§ 158.690 and 158.740,
since many of the higher tiered data will
not be required unless the results from
the lower tiered studies indicate a
concern for adverse effects.
4. Improving utility of the part 158
data tables. As described in the Notice
of Proposed Rulemaking on
Conventional Pesticides (70 FR 12276,
March 11, 2005), EPA has proposed to
reorganize and reformat part 158
subpart A (General Provisions) and
subpart B (How to Use Data Tables), and
reorganize and redesignate subpart D
(Data Requirement Tables) into several
individual subparts (see Table 1 in Unit
VI). In the proposed reorganization,
subpart L is designated for biochemicals
(§ 158.900) and subpart M (§ 158.1000)
is designated for microbials. Within
both subpart L and M, there are
definitions, examples, applicability, and
then the series of data requirements in
tables addressing product chemistry,
residue chemistry, human health
assessment or toxicology, nontarget
organism, and environmental fate.
Many of the revisions proposed in
this document are intended to improve
the usefulness of part 158 data tables by
better identifying the specific data
requirements that could apply to a
particular pesticide application. As with
the original design of part 158 in 1984,
given the variety in pesticide chemistry,
exposure, and hazard, these revisions
are intended to retain a fair amount of
flexibility in their application, while
improving clarity and transparency to
the regulated community.
5. Reducing burdens where consistent
with need for data. In proposing new
and revised data requirements, EPA
expects that fewer data waivers will be
needed where the issue is well resolved,
e.g., straight chain lepidopteran
pheromones (SCLPs), and physical
chemical properties criteria outlined in
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test notes when data are not required.
There are also more transparent test
notes indicating when data are required,
while providing assistance to avoid
generation of data where unnecessary.
There is also an opportunity to reduce
cost of preparation of waiver requests by
providing pre-submission/postsubmission meetings where appropriate.
D. What are Some of the Benefits of this
Proposal?
Discussed in more detail in the
document entitled ‘‘Economic Analysis
of the Proposed Change in Data
Requirements Rule for Biochemical and
Microbial Pesticides,’’ which is
available in the docket for this
rulemaking (Ref. 6), the following
briefly highlights the benefits
anticipated from this proposal:
1. More refined assessments mean
clearer understanding of real risks.
EPA’s current applicator/user exposure
data base is not comprehensive,
especially regarding exposures to
pesticides in nonagricultural settings.
The new data that would be collected
under this proposal would allow the
Agency to conduct improved exposure
assessments for applicators/users (i.e.,
especially for insect repellents). This
will benefit growers, other workers, and
consumers by allowing EPA to make
better informed regulatory decisions
that are neither too stringent nor too
lenient.
2. Clarity and transparency to
regulated community means savings.
The enhanced clarity and transparency
of the information presented in part 158,
subparts L and M should enhance the
ability of industry to avoid wasted time
and effort. Registrants may save time
and money by understanding when
studies are needed. This should allow
products to enter the market earlier,
thereby registering safer pesticides
sooner and potentially reducing risks as
well as increasing profits. The addition
of some data requirements is likely to
further communicate to domestic and
world-wide marketplaces that pesticide
products and items treated with them
are safer, thus enhancing the reputation
of American agricultural and
nonagricultural products and registered
pesticides as tools for public health.
3. Enhanced international
harmonization means less duplication.
EPA participates with OECD countries
in the development of harmonized
international standards and, to the
extent possible, we have included these
revisions in our proposal. The OECD
Biopesticide Steering Group has agreed
to use U.S. EPA Harmonized Guidelines
for the conduct of microbial pesticide
studies and we continue to work
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together to harmonize our approach to
evaluating and reviewing these data.
However, because other OECD countries
do not use the tiered approach to the
data requirements, but instead decide
on the data needed for registration on a
case-by-case basis, there may be
differences in the actual data required
for registration for the United States
compared with other OECD countries.
We are presently working with key
OECD biopesticide regulatory
representatives to develop OECD
guidance for waiving data, which will
bring actual data requirements closer
together. OECD has also recognized
pheromones, a certain type of
biochemical pesticide, as warranting a
separate, unique set of reduced data
requirements similar to the U.S. data
requirements.
4. EPA information assists other
communities in assessing pesticide
risks. Scientific, environmental, and
health communities find pesticide
toxicity information useful to respond to
a variety of needs. For example, medical
professionals are concerned about the
health of patients exposed to pesticides;
poison control centers make use of and
distribute information on toxicity and
treatment associated with poisoning;
and scientists use toxicity information
to characterize the effects of pesticides
and to assess risks of pesticide
exposure. Similarly those responsible
for protection of nontarget wildlife need
reliable information about pesticides
and assurance that pesticides do not
pose an unreasonable threat. The
proposed changes will help the
scientific, environmental, and health
communities by increasing the breadth,
quality, and reliability of Agency
regulatory decisions by improving their
scientific underpinnings.
5. Better informed users means
informed risk-reduction choices. Better
regulatory decisions resulting from the
proposed changes should also mean that
the label will provide better information
on the use of the pesticide. A pesticide
label is the user’s direction for using
pesticides safely and effectively. It
contains important information about
where to use, or not use, the product,
health and safety information that
should be read and understood before
using a pesticide product, and how to
dispose of that product. This benefits
users by enhancing their ability to
obtain pesticide products appropriate to
their needs, and to use and dispose of
products in a manner that is safe and
environmentally sound. Farmers (as
well as other applicators/users) may
benefit from label information based on
the data submitted to the extent it helps
inform their decisions about whether or
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how to use particular pesticides to avoid
potential exposure.
E. How will this Proposal Affect Existing
Registrations?
• This proposal codifies existing
practices by requiring data that are
necessary to complete a risk assessment
that are not included in the current data
requirements.
• This proposal imposes new
requirements for future registrations, as
is the case for applicator/user exposure
data to assess impacts from insect
repellents.
• In rare circumstances, the Agency
may find it necessary to call in data on
certain existing registrations, as
warranted by emerging risk issues.
F. Request for Comments
The Agency invites the public to
provide its views on the various options
proposed or present any data or
information for the Agency to consider
during the development of the final
rule. Specifically, the Agency welcomes
specific comments on the following
topics of particular interest to the
Agency.
The Agency welcomes specific
comments on the need for, value of, and
any alternatives to, the data
requirements described in this
document to meet its mandates.
The Agency welcomes comments on
the scientific basis of this proposed rule.
The Agency welcomes specific
comments on the clarity of the proposed
data requirements for biochemical and
microbial pesticides and the
relationship between the proposed data
requirements and EPA’s statutory
determinations.
The Agency welcomes specific
comments on the transparency of the
proposed definitions, examples, and
applicability for both biochemical and
microbial pesticides.
The Agency welcomes comments on
its economic analysis of the proposed
rule, as well as on its underlying
assumptions, economic data, and highand low-cost options and alternatives.
Describe any assumptions and provide
any technical information and data used
in preparing your comments. Explain
estimates in sufficient detail to allow for
it to be reproduced for validation. As
indicated in Unit V.B.1, EPA’s
underlying principle in developing the
proposed revisions has been to strike an
appropriate balance between the need
for adequate data to make the statutorily
mandated determinations and informed
risk management decisions, while
minimizing data collection burdens on
biochemical and microbial pesticide
applicants.
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VI. Background on Regulation of
Biochemical and Microbial Pesticides
and Preparation of this Proposed Rule
A. Background of Regulating
Biochemical and Microbial Pesticides
The Agency finalized the data
requirements to support the registration
of biochemical and microbial pesticides
(49 FR 42856, October 24, 1984) more
than 20 years ago. When promulgated in
1984, EPA distinguished ‘‘biochemical
and microbial pesticides’’ from
‘‘conventional chemical pesticides’’ by
‘‘their unique modes of action, low use
volume, target species specificity or
natural occurrence.’’ EPA recognized
that biochemical pesticides are
inherently different from conventional
pesticides since they are generally
naturally-occurring and have a nontoxic mode of action.
As a result, biochemicals are expected
to pose lower potential risk compared to
conventional pesticides. Due to the nontoxic mode of action and low risk to
humans, certain studies are not
included in the Tier I data requirements
for biochemical pesticides. This
adjustment in the tiered data
requirements was intended to serve as a
safety mechanism. If Tier I testing
indicates a toxic mode of action, the
biochemical would be treated as a
conventional pesticide, and virtually the
same toxicology and residue data would
be required as is required for a
conventional pesticide.
The Agency has confirmed in the past
20 years of regulating biochemical
pesticides that indeed biochemical
pesticides can be classified and
regulated with the data requirement
tables that have been designated for
biochemical pesticides. The Agency
recognizes that at the time of
application for registration there are
instances where a biochemical may not
fit the biochemical category and in such
cases the Agency evaluates the pesticide
in question as a conventional pesticide.
Ultimately, if a pesticide were to exceed
the criteria established for a biochemical
pesticide, the data requirements in the
higher tiers would be required and the
process would take longer than if the
application were made as a
conventional pesticide, since all data
requirements would not be clearly
identified from the onset.
Microbial pesticides are living
organisms and, as such, present much
different risk concerns than chemical
toxicants. The main concern for a
microbial pesticide is whether it could
survive within, and be pathogenic to, a
nontarget species or humans. As a
result, required studies specifically
address the potential for these unique
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risks. Some microorganisms do produce
toxins. If comparisons of the
microorganisms indicates that
taxonomically similar microorganisms
have been reported to be pathogenic, the
data set is configured to allow for use of
conventional toxicity testing if needed
to evaluate any toxins.
B. History of Development of
Biochemical and Microbial Pesticide
Data Requirements and Guidelines
1. Biochemical pesticides history for
regulatory activities. The following
provides the history in the regulatory
development of the data requirements
for biochemical pesticides since 1984.
• 1984—Promulgation of 40 CFR part
158 subpart A: § 158.65 Biochemical
and Microbial Pesticides and subpart D:
§ 158.690 Biochemical Pesticide Data
Requirements and Microbial Data
Requirements (49 FR 42856, October 24,
1984).
• 1987—Report of SAP
Recommendations: A Set of Issues Being
Considered by the Agency in
Connection with Proposed Revision to
Subdivision M, Immunotoxicity Testing
of Biochemical Pest Control Agents (Ref.
7).
• 1989—Issuance of Subdivision M of
the Pesticide Testing Guidelines
Microbial and Biochemical Pest Control
Agents (Ref. 8). Although titled as such,
this guideline did not include a
discussion on biochemical guidelines.
The Agency still relies on 1982
Pesticide Assessment Guidelines
Subdivision M Biorational Pesticides
(Ref. 9) for the guidelines pertaining to
biochemicals (880 series) if there is not
a designated guideline in the
conventional pesticide series (i.e., 870
series and 850 series).start here next
• 1994—Presentation to SAP to
discuss data requirements for all
pesticides, including biochemical and
microbial pesticides (Ref. 4). Some data
requirements were presented to support
conventional pesticides, i.e., applicator/
user exposure data to support insect
repellents (Ref. 10).
2. Microbial pesticides history for
regulatory activities. The following
provides the history in the regulatory
development of the data requirements
for microbials since 1984.
• 1984—Promulgation of 40 CFR part
158 subpart A: § 158.65 Biochemical
and Microbial Pesticides and subpart D:
§ 158.690 Biochemical Pesticide Data
Requirements and Microbial Pesticide
Data Requirements (49 FR 42856,
October 24, 1984).
• 1987—Presentation to SAP in 1987
for microbial pesticides in preparation
for updating the guidelines (Ref. 7) on
immunotoxicity testing.
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• 1989—Issuance of Subdivision M of
the Pesticide Testing Guidelines
Microbial and Biochemical Pest Control
Agents (Ref. 8). This was a culmination
of the 1987 SAP and public comments.
• 1994—Presentation to SAP to
discuss data requirements for all
pesticides, including biochemical and
microbial pesticides (Ref. 4).
This proposed rule proposes to codify
the draft data requirements outlined and
presented to the FIFRA SAP in 1994 and
in subsequent meetings. However, EPA
is proposing certain revisions for
biochemicals that are also discussed
fully in the Agency’s proposal for
conventional chemicals (70 FR 12276,
March 11, 2005) (Ref. 5). The Agency
developed a complete list of data
requirements for biochemicals and
microbials and the year each were
presented to FIFRA SAP (Ref. 11). This
reference, the SAP final reports, and
relevant documents presented to the
SAP are available in the docket for this
proposed rulemaking.
C. EPA Activities in Preparation for this
Proposed Rule
1. Consideration of redesigning data
requirement tables. While preparing for
this proposed rule, the Agency
considered redesigning data
requirements based on subcategories of
biochemical and microbial pesticides.
Each subcategory was evaluated based
on mode of action and potential for risk
to human health and the environment,
with each subcategory requiring
different data to support registration.
The subcategories for biochemical
pesticides were as follows: pheromones
(including arthropod, lepidopteran, and
straight chain lepidopteran
pheromones), growth regulators (insect
and plant), repellents (insect and
others), and other biochemicals (which
includes all other biochemicals). The
microbial pesticides includes the
following subcategories: protozoa,
viruses, bacteria, and fungi.
In the economic analysis for this
proposed rule, the Agency analyzed the
test cost data submitted based on each
subcategory to determine the different
data requirements (Ref. 12). Based on
the analysis, the Agency decided it was
more appropriate to make the test notes
more clear and transparent, and only
update the data requirement tables
without redesigning them based on
subcategory.
2. Consistencies between current part
158 and proposed part 158 design of
data requirement tables for biochemical
and microbial pesticides. EPA is
proposing to continue using the tiered
testing system, as given in the current
§ 158.690 and § 158.740. For these
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specific types of pesticides, it is
appropriate to ask for studies in a tiered
scheme because many of the higher
tiered data will not be required unless
the results from the lower tiered studies
indicate a concern for adverse effects.
3. Consultations with stakeholders.
During the pre-rulemaking process, the
Agency actively sought consultations
with industry, academia, and non-profit
organizations (i.e., environmental
groups) on the current regulatory
requirements for data and requested
input on the universe of possible
changes to the regulatory text. For
parties interested in discussing the
development of this rule with EPA,
consultations were held in-person, by
telephone conference, and via-email.
During these pre-proposal stage
consultations, the Agency did not
request feedback on the changes being
proposed today, whether the proposed
changes are newly imposed, newly
codified data, or revisions to existing
data requirements. Feedback from these
consultations included the following
topics: existing data requirements,
industry burden in fulfilling data
requirements, tiered testing approach,
and issuance of guidance specific to test
protocols. All the stakeholder comments
are available in the docket (Ref. 13).
D. Consultations with Applicants
In an effort to improve transparency,
increase efficiencies and reduce
burdens, EPA is announcing a policy to
provide assistance to applicants when
needed in determining what data or
information are appropriate to support
registration of a biochemical or
microbial pesticide. EPA is encouraging
applicants to request pre-submission
meetings to discuss these data issues.
EPA is also announcing its intent to
provide assistance to applicants in some
narrow circumstances in preparation of
an applicant’s data waiver after
submission of an application.
EPA notes that applications for
biochemical and microbial pesticides
frequently involve substances that
present low risk (i.e., naturallyoccurring, non-toxic mode of action,
minimal exposure). Data requirements even as proposed—may overstate the
Agency’s need, or may be satisfied by
existing data in the open literature or
other available data or information. In
some cases, the applicant may not be
aware of a potential rationale for a
waiver or be able to identify available
data or information that may satisfy a
data requirement in lieu of generating
new data. Thus, EPA encourages
applicants to seek pre-submission
meetings to discuss the appropriate data
or information to support their product
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and the opportunity for requesting data
waivers.
1. Pre-submission process. During a
pre-submission meeting, EPA may be
aware that certain data requirements are
already satisfied by available data or
information. Sources of existing data
include public literature and/or studies
submitted by another registrant, which
may be cited with data compensation
procedures. EPA may also be aware of
sound scientific rationales that certain
data requirements should not be
imposed. For example, the question the
required data is intended to answer
might be addressed by a combination of
other information or data, and therefore
might be able to be waived. In either
case, during the pre-submission
meeting, EPA would discuss with the
applicant the grounds for citing other
information or data to conclude that a
data requirement has been met or the
grounds for requesting a waiver where
other information or data otherwise
addresses the need for a specific piece
of data required by the regulations have
been satisfied. The applicant may then
submit an application based on the
discussion with EPA. The application
should include a signed copy of the
minutes of the pre-submission meeting
listing each data requirement and the
reason why EPA and the company
believe a waiver is appropriate. The
applicant is encouraged to submit a
copy of the pre-submission meeting
minutes to EPA for concurrence prior to
submission of its application for a
waiver.
To some extent, EPA currently offers
this assistance to applicants and is
simply encouraging applicants to
request pre-submission meetings and
suggesting a process for ensuring
consistent reflection of discussions at
the pre-submission meeting.
2. Post-submission process. Even after
submission of an application for
registration, EPA may find that either of
these scenarios exist (i.e., basis for citing
to other data/information or waiver of a
data requirement). Again, EPA may
discuss these issues with the applicant
and the applicant may choose to amend
its application by citing to other data/
information or requesting a waiver.
EPA is also announcing its intention
to assist applicants in the actual
preparation of a data waiver in some
narrow circumstances. Specifically, in
the course of reviewing an application,
EPA may find that in its judgment, data
otherwise required by part 158 would
not be necessary to grant the application
or are available from other sources. EPA
would notify the applicant and explain
the basis for its belief in writing. If the
data are compensable or exclusive in
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use, the applicant may submit EPA’s
letter with the appropriate offer to pay
or an authorization, as an amendment to
its application. If the Agency explains in
its correspondence that the data may be
waived, the applicant may use EPA’s
correspondence to support a waiver
request by signing the correspondence
and submitting it as an amendment to
its application. Because the
correspondence only includes citation
or discussion of existing data or
information, EPA is proposing not to
consider such amendments to an
application to be ‘‘data’’ subject to the
formatting provisions of § 158.32(a) as
proposed on March 11, 2005 (70 FR
12276).
This pre-submission and postsubmission process for ensuring that the
data requirements are either satisfied or
waived is specific to the review of
biochemical and microbial registration
applications, due primarily to the
specific nature and circumstances
unique to these pesticides (e.g.,
information already known to the
Agency) and thus the Agency does not
anticipate this process being widely
applicable to other types of pesticides,
such as conventional or antimicrobial
pesticides.
EPA notes that in providing this
assistance during the pre-submission
and post-submission process, it will
only consider readily accessible
information, such as information found
in Agency databases, and will not
search for applicable information, data,
or literature. Further, although
intending to help applicants in
supporting their applications, EPA does
not encourage applicants to rely on this
process to fill informational data gaps;
doing so may be at the expense of timely
review or may ultimately result in
rejection of an application or petition.
Finally, providing assistance in this
manner does not effectively allow
applicants to circumvent the data
requirements or the requirement to
submit a waiver of a data requirement.
The applicant must at all times submit
the waiver request; EPA is simply
providing assistance in what
requirements are likely to be waived for
a particular product or, in some narrow
circumstances, assistance in the
preparation of the waiver request.
Throughout these mechanisms EPA is
flexible in implementing the regulation.
Thus, the waiver provisions currently
codified and the recent proposed
amendments to the waiver provisions
do not need to be amended.
One of the benefits of providing this
pre-submission and post-submission
assistance is the reduction in burden.
Prior to finalization of this proposed
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rule (e.g., codifying that some data may
no longer be required or adding
conditions that result in data not being
required), the number of opportunities
for requesting waivers or citing to
existing data will not change. Thus,
providing assistance in this manner
prior to finalization of this proposed
rule may avoid the generation,
processing and review of unnecessary
data, and thereby ultimately save the
Agency and applicant expenses, while
providing the same level of protection
for human health and the environment.
In addition, although this proposal
attempts to refine the test notes in order
to be more transparent when data are
required and necessary to support
registration, there will continue to be
opportunities to reference existing data
or information or request waivers based
on information that may be readily
accessible to the Agency, and again
avoid the generation, processing, and
review of unnecessary data or
information. Thus, the Agency expects
to reduce burdens on both the
applicants and EPA during and after the
rulemaking process.
E. Agency Coordination with the APHIS
Permitting Process
As a result of the comments received
during the Interagency review process,
the Agency and USDA have discussed
the registration process of microbial
pesticides and the need for coordination
when an Animal and Plant Health
Inspection Service (APHIS) movement
permit under 7 CFR part 340 is required
by USDA. USDA suggested that the
registrants should be required to submit
a copy of the applicable APHIS permits
as part of the registration application to
EPA. The Agency is seeking public
comment on the most appropriate
method to ensure APHIS permitting and
EPA registrations are coordinated. In
particular, EPA is interested in your
specific suggestions on whether there
should be a requirement for pesticide
registration applicants to include copies
or otherwise attest to the applicability of
and their compliance with the APHIS
requirements when they submit their
registration application to EPA.
F. Differences Between the Proposed
Biochemical Data Requirements and the
Proposed Conventional Data
Requirements
There are several revisions that were
included in the proposal to amend part
158 for conventional pesticides, but
were considered not appropriate for
biochemical pesticides. For example,
neurotoxicity studies (including acute,
subchronic, delayed, and developmental
neurotoxicity studies; OPPTS Test
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Guidelines 870.6100, 870.6200,
870.7620, etc.) are required to support
conventional pesticides. In addition, the
recent proposal (70 FR 12276, March 11,
2005) identifies developmental
neurotoxicity to be critical in some
cases. If the Agency identifies a
biochemical pesticide to be a potential
neurotoxicant, then the Agency would
evaluate the pesticide as a conventional
pesticide, and it would then require the
neurotoxicity data to support
registration. The Agency prepared an
overview of the proposed data
requirements for biochemical pesticides
as compared to conventional pesticides
(Ref. 14).
G. Similarities Between Both
Biochemical and Microbial Proposed
Rule Development and Proposed Rule
for Conventional Pesticides
The Agency proposes to retain certain
data requirements when they are
appropriate. For instance, biochemical
pesticides data requirements for product
chemistry are the same as is required for
conventional pesticides (§ 158.320
through § 158.355).
Certain revisions for proposed
conventional pesticides (70 FR 12276,
March 11, 2005) were considered
appropriate for biochemicals and/or
microbials and are included in this
proposed rule, i.e., registrations
introducing significant exposure require
applicator/user exposure data. As
previously mentioned, the consistent
designation of CR and R within the data
tables remains the same as it is in the
current part 158 for both conventional
pesticides and microbial and
biochemical pesticides. The proposed
conventionals retains the CR and R
designation, and this proposed rule
retains this designation as well, within
the data tables.
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H. Proposed Amendments and
Reference to Harmonized Guidelines
The following units VII and VIII
identify the proposed revisions to the
current data requirements for
biochemicals and microbials. In each
preamble unit, the Agency explains the
basis for the proposed amendments and
for ease of reference to the public,
identifies the harmonized guideline that
is applicable to the proposed data
requirement. EPA is not proposing
changes to these harmonized guidelines
as they have gone through a public
review. The reference is simply for ease
in understanding the proposed
revisions.
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VII. Biochemical Pesticide Data
Requirements (Subpart L)
A. Definition of Biochemical
The Agency is proposing to revise the
definition of biochemical. Although the
current definition provides examples of
biochemicals, it does not really explain
what a biochemical is. The language in
the current definition was constrained
by the need for including microbial
pesticides in the same definition that
defined biochemical pesticides. The
new format for this regulation allows for
a separation of the two classes of
pesticides. The proposed definition of
biochemical is intended to reflect a
more useful and transparent definition,
in accordance with the original
scientific rationale for creating the
biochemical class of pesticides while
being consistent with the examples. The
current definition is listed in § 158.65
and reads as follows:
Biochemical and microbial pesticides are
generally distinguished from conventional
pesticides by their unique modes of action,
low use volume, target species specificity or
natural occurrence. ... (a) Biochemical
pesticides include, but are not limited to,
products such as semiochemicals (e.g., insect
pheromones), hormones (e.g., insect juvenile
growth hormones), natural plant and insect
regulators, and enzymes. When necessary the
Agency will evaluate products on an
individual basis to determine whether they
are biochemical or conventional chemical
pesticides.
EPA is proposing to relocate the
definition of biochemical to § 158.900,
which would immediately precede the
data requirements in part 158 for the
respective categories of biochemicals.
EPA is also proposing to amend the
definition so that it would state the
following:
A biochemical pesticide is a pesticide
that:
(1) Is a naturally-occurring substance or
structurally similar and functionally
identical to a naturally-occurring substance;
(2) has a history of exposure to humans
and the environment demonstrating minimal
toxicity, or in the case of a synthetically
derived biochemical pesticides, is equivalent
to a naturally-occurring substance that has
such a history; and
(3) Has a non-toxic mode of action to the
target pest(s).
EPA is proposing to continue the
requirement that a biochemical
pesticide be naturally-occurring. In
addition, based on a long established
policy, EPA is proposing to include a
clarification that a ‘‘naturally-occurring’’
biochemical pesticide may be
synthetically produced if it is
‘‘equivalent’’ (structurally similar and
functionally identical) to the naturallyoccurring chemical. A synthetically
derived chemical may often be more
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pure or economically feasible to
produce but have the same properties as
its naturally-occurring equivalent. An
example of a synthetic substance that
meets the criteria for classification as a
biochemical is an insect pheromone
manufactured by man. These insect
pheromones are structurally and
functionally identical to the substances
that are produced by the insects, but the
currently registered products are not
naturally-occurring because it would be
very difficult to extract them directly
from an insect in a usable form.
Second, the current regulation does
not explicitly indicate that inherent
non-toxicity is a means of defining a
biochemical. EPA is proposing to add a
criterion to the definition of
biochemical that requires that there be
a history of exposure to the naturallyoccurring pesticide or, for syntheticallyderived pesticides, to the equivalent
naturally-occurring pesticide, and that
exposure demonstrates minimal
toxicity. The original intent for
specifying natural occurrence in
§ 158.65 was to allow EPA to use
information derived from the pesticide’s
natural exposure to humans and nontarget species to decide if the pesticide
is inherently toxic. This is described in
the 1982 Pesticide Assessment
Guidelines, Subdivision M for
Biorational Pesticides, section
V(A)(2)(1) (Ref. 9), which states that the
fact that the chemical is naturallyoccurring is to be used to predict
whether ‘‘these compounds are
generally not innately toxic.’’ Therefore,
the criterion for having a history of
adequate exposure was added in order
to have confidence that if the naturallyoccurring pesticide were not ‘‘innately’’
toxic, it would have to be present in the
environment at sufficient levels and
locations to predict significant exposure
to humans and/or non-target species. If
the pesticide is naturally-occurring but
inherently toxic, EPA would use the
data requirements for the conventional
pesticides to ensure it could conduct an
adequate assessment of the risks from
the proposed use of the pesticide.
Thus, rather than giving the
impression that natural occurrence
alone defines whether the pesticide
should be classified as a biochemical
pesticide, the Agency is proposing to
include the criterion that there be a
history of exposure demonstrating
minimal toxicity. In order to make this
determination, the naturally-occurring
pesticide or the naturally-occurring
equivalent to the synthetically derived
pesticide must be present in the
environment in sufficient quantities so
that if it is innately toxic, there would
be a good chance that this toxicity
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would already have been recognized
because of its effect on humans or
representative non-target organisms.
EPA has often used public literature to
demonstrate that the substance is either
widely used, and/or widely known
(supported by extensive information
and low toxicity) as part of the decision
whether a pesticide may be adequately
reviewed using the reduced data set for
biochemical pesticides. The natural
occurrence of a pesticide does not
necessarily mean that it has a non-toxic
mode of action to the target pest. An
example might be pyrethrins, which are
naturally-occurring toxins that occur in
chrysanthemum plants. The new criteria
in the biochemical definition would
clearly allow us to classify this as a
conventional chemical pesticide that
would be subject to the conventional
pesticide data requirements, which is
consistent with past Agency decisions.
Third, the current regulation refers to
a unique mode of action, which is an
attempt to describe the mode of action
of both microbial and biochemical
pesticides together. EPA is proposing to
add a criterion to the definition of
biochemical to better describe that the
unique mode of action for biochemical
pesticides must be one that is non-toxic
to the target pest(s). This was the
original intent for the biochemical
pesticide mode of action as described in
the 1982 Pesticide Assessment
Guidelines, Subdivision M for
Biorational Pesticides. That guideline
explained in section I(A)(1) (Ref. 9) that
‘‘some of the characteristics that
typically distinguish biorational from
conventional pesticides are their unique
non-toxic mode of action, ...,’’ and in
section V(A)(2)(1) that a characteristic of
biochemical pesticides is that ‘‘their
pesticidal action is not the result of
target organism toxification.’’ Thus, the
third element of the definition adds that
the biochemical must have a non-toxic
mode of action to the target pest. This
toxic mode of action criterion would
preclude pyrethrins and other clearly
toxic naturally-occurring pesticides
from being classified as biochemicals.
In addition to the proposed language
noted previously, EPA is proposing to
amend the examples provided in the
current definition of biochemical to
better represent the kinds of
biochemical pesticides we have actually
seen since the original rule was
published and move the examples from
the actual definition to a subsequent
paragraph. The proposed definition
removes hormones from the example
list because hormones fall into the
growth regulator class, which is already
in the list. The new ‘‘Examples’’ section
is proposed to read as follows:
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Biochemical pesticides include, but are not
limited to: (1) Semiochemicals (e.g., insect
pheromones and kairomones), (2) natural
plant and insect regulators, (3) naturallyoccurring repellents and attractants, and (4)
enzymes.
At the present time, the Agency will
review requests for classification as a
biochemical pesticide, but does not
believe this needs to be part of the
regulatory language because the
proposed revised definition is much
more definitive than the current
definition.
As a final note, although not always
the case, EPA recognizes that
biochemical pesticides tend to have a
limited range of target species, are often
effective against their target pest(s) in
relatively low quantities, and usually
decompose rapidly after application in
the environment.
B. Applicability of Biochemical
Pesticide Data Tables
EPA is also proposing to use table
descriptors NR (not required), R
(required), and CR (conditionally
required) to be used as markers along a
spectrum of the likelihood that a data
requirement applies. In other words, it
should be assumed that a required (R)
data requirement is required typically
all the time. There may be some narrow
or rare conditions identified in test
notes when data are not required. For
example, acute oral toxicity data are
required to support registration for
biochemical pesticides unless the
proposed pesticide is a gas or highly
volatile (which is rare). In contrast, a
conditionally required (CR) data
requirement is less likely to be triggered
compared to a required (R) data
requirement. Conditionally required
data are more likely to include test notes
indicating conditions when data are
typically required. For example, the 90–
day dermal toxicity test is currently
conditionally required (CR) for
biochemical pesticides. The test note
indicates it is required (R) to support
uses involving purposeful application to
human skin or which would result in
comparable prolonged human exposure
to the product (e.g., insect repellents).
Specific criteria are identified with the
test note.
C. Product Chemistry Data
Requirements
1. General. The Agency uses product
chemistry information to determine
whether impurities of toxicological or
environmental concern are present in
biochemical pesticides and their
formulated products. Product chemistry
data requirements include product
identity and composition, the physical
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and chemical characteristics of data on
the pesticide, the identity of any
intentionally added ingredients, and
impurities in the final pesticide
product.
The Agency is continuing to list the
data requirements in the table for
product identification, description of
starting materials, production and
formulation process, discussion of
formation of impurities, preliminary
analysis, certified limits, and physical
and chemical characteristics, as
currently listed in § 158.690. The
following is a discussion about the
changes from the current data
requirements to support ‘‘biochemical
product analysis data requirements’’ to
the proposed ‘‘biochemical product
chemistry data requirements’’ for
biochemicals. The revised title of the
proposed table more accurately reflects
the current types of data required to
support biochemical pesticides.
In addition, the proposed rule for
conventional pesticides (70 FR 12276,
March 11, 2005) identifies the following
sections where this proposed rule will
also require the same information/data
and are indicated in the test notes
within the proposed product chemistry
data requirement table: §§ 158.320,
158.325, 158.330, 158.335, 158.340,
158.345, 158.350, 158.355.
2. Proposed product chemistry data
requirements. The Agency proposes to
codify one study (particle size, fiber
length, and diameter distribution) and
to make minor revisions to existing data
requirements to support product
chemistry data requirements. The
Agency is also proposing to require
studies to support experimental use
permits (EUPs) as well as registration for
certain studies, (i.e., certified limits). In
addition, certain studies (i.e.,
enforcement analytical method) would
require a different test substance (for
example, TGAI or both EP and MP). One
study, which is currently required to
satisfy environmental fate and
expression data requirements, is
proposed to be moved from
environmental fate and expression to
the product chemistry data
requirements (ultraviolet (UV)/light
absorption) table. The Agency is also
proposing to delineate the physical and
chemical properties into subcategories,
depending on the formulation type (e.g.,
solid versus liquid) and provide test
notes identifying conditions when data
are required (i.e., flammability). In other
words, the current product chemistry
data requirement table lists physical and
chemical properties as one data
requirement, whereas the proposed rule
identifies the individual studies that
make up physical and chemical
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properties (e.g., color, odor, vapor
pressure, pH). Additional test notes
concerning the physical and chemical
properties identifying when each data
requirement is required (i.e., solid
versus liquid at room temperature,
water insoluble substances (10-6 grams/
liter (g/l)) are also included.
i. New requirements. None.
ii. Newly codified requirements—
particle size, fiber length, and diameter
distribution. The Agency proposes to
add the conditional requirement (CR)
for data on particle size, fiber length,
and diameter distribution. This data
requirement is proposed to be
conditionally required (CR), the
condition being that the test substance
is water insoluble (<10-6 g/l) or fibrous
with diameter ≥ 0.1 mm (micrometer).
Data from this study are needed to
complete the environmental fate
assessment to estimate potential
pesticide drift to nontarget areas.
iii. Revisions to existing requirements.
a. ‘‘Certification of limits’’ data are
currently conditionally required (CR) to
support all proposed use patterns/
applications, except for EUPs for
nonfood crops. The Agency proposes to
change the conditionally required (CR)
to required (R) ‘‘Certified limits’’ data to
support proposed use patterns to ensure
we have proper product chemistry
information on all registrations for
enforcement purposes.start
b. UV/visible light absorption. The
Agency currently requires (R) these data
to satisfy one of the nontarget organism,
fate and expression data requirements.
The Agency proposes to relocate this
data requirement from environmental
fate and expression data tables to the
proposed product chemistry data table.
The endpoints measured by this data,
characterization, and identification of a
compound are more appropriately
considered product chemistry data. This
is not a new data requirement, merely
a relocation. This information will be
used in conjunction with the
‘‘photodegradation in water’’ study to
determine if photodegradation is a
possible route of dissipation in the
environment. In order for a pesticide to
undergo direct photolysis in the
environment, it must absorb energy in
the wavelength range emitted by
sunlight. The UV/visible light
absorption spectrum will indicate
whether the pesticide is absorbed in this
range.
c. Revision of names. The Agency
proposes to revise names of certain
studies to correspond with OPPTS Test
Guidelines (Ref. 2) and to synchronize
with the name changes taking place in
the updating of part 158 for
conventional pesticides. The following
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three name changes are proposed in this
section: (1) ‘‘ Product identity’’ to
‘‘Product identity and composition’’; (2)
‘‘Discussion of formation of
unintentional ingredients’’ to
‘‘Discussion of formation of impurities’’;
and (3) ‘‘Manufacturing process’’ to
‘‘Description of starting materials,
production and formulation process.’’
D. Residue Chemistry Data
Requirements
1. General. The Agency is proposing
to codify two data requirements which
identify the use pattern under which
they are proposed to be required. EPA
is also proposing to consolidate the
nonfood use patterns into the following
four categories: terrestrial nonfood;
greenhouse nonfood; forestry; and
domestic outdoor, and to do so for all
residue data requirements except for
chemical identity and directions for use.
Those will remain conditionally
required (CR) for all uses. This would
not change the number of times the data
are required, but merely consolidate the
uses that have the same data required
under the same conditions.
In addition, the Agency is proposing
to delete the test note stipulating data
conditionally required (CR) if the
application rate of 0.7 ounces was
exceeded. This test note is no longer
considered relevant. Therefore, all the
proposed residue chemistry studies
would be required regardless of the
application rate. It was originally
incorporated in the data requirements as
explained in the October, 1982,
Subdivision M guidelines (pages 31 and
32, Section VI, Residue Analysis) as an
estimate of a ‘‘low application rate’’
since the original definition for
biochemical and microbial pesticides
(40 CFR 158.65) mentioned that they are
generally distinguished from
conventional pesticides by various
characteristics including ‘‘low use
volume.’’ The Agency has determined
that the key to whether residue data
(which is needed only to support a
numerical tolerance) are needed for
biochemical (and microbial) pesticides
is toxicity, not exposure by itself.
2. Residue data requirements— i. New
requirements. None.
ii. Newly codified requirements—a.
Nature of the residue: plants; livestock.
These data are currently not required
(NR) to support indoor food use. The
Agency, however, proposes to
conditionally require (CR) these studies
to support registration of indoor food
use. There have been instances where
certain biochemical pesticides are
applied to food crops indoors (e.g., for
treatment of stored potatoes), and these
potato peels are then fed to cattle for
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feed. Therefore, the nature of residues
on plants is needed to determine
potential residues on the treated crop.
The 0.7 ounces per acre restriction is no
longer a trigger for requiring the
submittal of data. The Agency also
proposes to eliminate ‘‘Nature of
residue: livestock’’ to support domestic
outdoor use, since the data are needed
for potential food uses outside of the
home, and domestic outdoor use is for
porches, patios, yards, home gardens,
etc. EPA also proposes to no longer
require testing on Pure Active
Ingredient Radio Labeled (PAIRA) but
instead to use the TGAI because it is
difficult to isolate pure active ingredient
from a naturally-occurring substance.
b. Residue analytical method. This
data requirement is currently
conditionally required (CR) for
terrestrial, aquatic, and greenhouse food
use with the 0.7 ounce per acre
limitation (data not required if applied
at rate less than or equal to) restriction.
The Agency proposes these data to be
required (R) for greenhouse use and
continue to conditionally require (CR)
data for terrestrial, aquatic, and indoor
food use but without the less than 0.7
ounce active ingredient (a.i.)/per acre/
year exemption. It would remain
conditionally required (CR) for indoor
food use. The residue analytical method
data are needed to address enforcement
issues, i.e. ability to measure the
pesticide.
iii. Revisions to existing
requirements—a. Chemical identity and
Directions for use. These data are
currently conditionally required (CR)
based on a series of conditions
including if the application rate exceeds
0.7 ounces (20 grams) active ingredient
per acre per year. EPA proposes not to
include the application rate conditions
(data required only if application rate
exceeds 0.7 ounce a.i./acre/year). EPA
proposes test note revisions for both the
chemical identity and directions for use,
but preserves one test note addressing
domestic outdoor use. However, EPA is
proposing to continue to conditionally
require (CR) this data only for all
biochemicals for which residue data are
required since chemical identity and
directions for use are considered to be
essential to understanding the pesticide.
The Agency has determined that
throughout the years of registration
activities for all biochemicals, the
chemical identity and the directions for
use information are always submitted
before processing the application. The
directions for use are included as part
of the labeling information along with
the submission.
b. Multiresidue method. Multiresidue
methodology data are currently part of
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the residue analytical method
requirement. The Agency proposes to
codify an existing multiresidue method
study (guideline 860.1360) and
designate it as a separate requirement.
These data, which are currently
submitted to support registration, are
important in designing pesticide
monitoring and enforcement programs.
In food monitoring programs, it is not
practical or feasible to test for
individual pesticides. Since the residue
analytical method requirement is
intended to refer to a method that is
specific for one pesticide (sometimes
called a ‘‘single residue method’’) and
the multiresidue procedures currently
used are designed to allow analysis of
as many pesticides as possible, it is
clearer to list these as two separate data
requirements. The test note indicates
that any analytical methodology must be
evaluated for its ability to detect
metabolites included in the tolerance
expression.
c. Magnitude of residue data. All the
studies in this category (guidelines
860.1400 through 860.1650) no longer
have the application rate of 0.7 ounces
a.i./per acre/ per year exemption.
d. Submittal of analytical reference
standards. The Agency currently
conditionally requires (CR) this data as
‘‘submittal of samples’’ as a product
analysis data requirement. The Agency
is proposing to revise the name to
‘‘Submittal of Analytical Reference
Standards’’ (quideline 860.1650) and
continue to conditionally require (CR)
the data. The requirement for submittal
of samples was moved to the residue
data requirements because it is
considered a residue data requirement
rather than a product analysis data
requirement. Biochemical pesticides are
generally of low toxicity because of their
non-toxic mode of action, but, if the
Agency does identify toxicity concerns,
then an analytical reference standard
requirement will be triggered to analyze
potential residues.
E. Human Health Assessment Data
Requirements
1. General. The current ‘‘Toxicology’’
data requirement is proposed to be
renamed from ‘‘toxicology’’ to ‘‘human
health assessment’’ to include
toxicology and applicator/user exposure
data requirements. Toxicology studies
are required by the Agency to assess the
hazard of the pesticide to humans and
domestic animals. These hazard data,
when combined with exposure data,
form the basis for the human health risk
assessment. For example, an insect
repellent registration would require
significantly more human health
assessment data compared to a
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application for SCLP. The duration of
the toxicity study approximates the
estimated duration of human exposure,
while considering species differences in
maturational milestones and overall life
span.
The proposed table in subpart L
(§ 158.950) contains the human health
assessment data requirements EPA
would rely on to identify potential
hazards to humans and domestic
animals for biochemical pesticides, and
is expected to improve the Agency’s
understanding of the potential pesticide
hazard to animals and humans,
including subpopulations such as
infants and children and possible
environmental effects. This proposal
retains the requirements for pesticides
in current 40 CFR 158.690, as well as
revisions that reflect the current
practices due to FQPA implementation
and the evaluation of regulating
biochemical pesticides.
The Agency is continuing to require
toxicity studies where use patterns
indicate high exposure, such as food use
biochemical pesticides, as well as
exposure studies required to support
certain use patterns (e.g., insect
repellents). The exposure data assess
exposure to both the person to and for
whom the repellent is being applied as
well as the person who is applying the
repellent (i.e., parent to child) and it
also assesses hand to mouth contact (i.e.
children), which often occurs under
these circumstances. Other toxicity
studies, e.g., 90–day dermal, 90–day
inhalation, 90–day oral toxicity for
nonfood use, etc., remain as
conditionally required on a case-by-case
basis, depending on the category of
pesticide (e.g., SCLPs, growth
regulators, repellents), the patterns of
use (food and nonfood), and estimated
exposure and the results of lower tiered
studies.
2. Human health assessment data
requirements. The following identifies
the revisions from the current
‘‘Biochemical pesticides toxicology data
requirements’’ in 40 CFR 158.690 to the
proposed ‘‘Biochemical pesticides
human health assessment data
requirements.’’ The title of the data table
has been revised to reflect that the
primary use of the data is to assess the
potential risk to humans. The proposed
revised table includes the toxicology
data requirements and exposure studies
(the latter to support insect repellent
uses). There are few new studies which
are proposed which were not identified
until the 1986 Science Advisory Panel
discussing applicator/user exposure
data requirements (Ref. 10) and
conditions under which data are
appropriate (except the companion
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animal safety data). The following lists
the individual data requirements, and
what the proposed rule requires and
when it requires these data. There is
also a discussion on why the Agency
proposes companion animal safety data
in this proposed rule as well.
i. New requirements.—a. Exposure
(applicator/user). The Agency proposes
exposure studies (guidelines 875.1000
through 875.1500) to be conditionally
required (CR). These data are triggered
when Tier I toxicology data indicate that
the biochemical may pose a hazard. The
Tier II human health assessment data
(toxicology and/or exposure)
requirements are not required if the
results from the Tier I toxicity studies
indicate no expected risk. The Agency
recommends that registrants consult
with the Agency prior to study initiation
to determine what exposure studies are
appropriate based on the nature of the
adverse effects seen in the Tier I data.
The following are the various types of
applicator/user exposure data that could
be required:
(1) Dermal exposure. The Agency
proposes to conditionally require (CR)
data for both outdoor and indoor dermal
exposure studies (guidelines 875.1100
and 875.1200) in order to estimate the
dermal exposure to persons directly
handling pesticides. Dermal applicator/
user exposure studies employ passive
dosimetry techniques which estimate
the amount of a pesticide impinging on
the surface of the skin. The amount of
pesticide potentially available for
absorption through the skin can be
estimated by trapping the material using
patches that absorb pesticides or by
removing the material that has
contacted the skin before it has been
absorbed.
(2) Inhalation exposure. To estimate
inhalation exposure to pesticide
residues, the Agency proposes to
conditionally require (CR) both outdoor
and indoor inhalation exposure studies
(guideline 875.1300 and 875.1400). It
has become apparent to the Agency that
insect repellents when applied often
result in inhalation exposure to the user
(either to the person it is being applied
(e.g., child) as well as to the person
applying the insect repellent (e.g.,
adult)) and therefore the Agency would
like the flexibility to require these data
for this use when triggered by results
from lower tier studies or estimated
exposure.
(3) Biological monitoring. Data from
biological monitoring studies (guideline
875.1500) provide the Agency with
estimates of the internal dose or amount
of a pesticide in the body. EPA proposes
to allow the submission of biological
monitoring data in addition to, or to
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satisfy, dermal or inhalation exposure
data requirements provided the human
pharmacokinetics of the pesticide
residue are sufficiently understood to
permit calculation to determine the total
internal dose. Biological monitoring
offers the advantage of assessing the
actual internal dose, as opposed to the
estimated exposure or amount of
pesticide coming in contact with the
surface of the skin or available for
inhalation in the lungs as measured
using passive dosimetry techniques. For
example, biological monitoring could
consist of evaluating blood for
cholinesterase activity; if it is low in a
blood sample, the person may have been
exposed to a cholinesterase inhibitor by
any route including dermal or
inhalation. Also, biological monitoring
may indicate whether a given substance
has been absorbed through the skin or
inhaled in enough quantities to be of
concern.
b. Companion animal safety data.
Companion animal safety data
(guideline 870.7200) is being proposed
to be part of conditionally required (CR)
special testing. This data would be
triggered if the product’s use would
result in exposure to domestic animals
through, but not limited to, direct
application (e.g., topical application as
in insect repellents) or consumption of
treated feed. This new data requirement
is based on recent Agency experiences
with biochemical pesticides,
specifically, that there are currently no
data requirements addressing potential
toxicity to domestic animal species from
biochemical pesticides. Fulfillment of
this conditionally required data would
address such potential risk concerns.
This is considered part of the human
health battery of studies, as it is
considered for conventionals.
ii. Newly codified data
requirements.—a. Hypersensitivity
incidents. Currently, the Agency
conditionally requires (CR) these data
when they are reported. The Agency
proposes to augment this data
requirement to include incidents to be
reported from conditionally required
(CR) to required (R) for all preregistered
(EUP’s) and registered products.
Incidents can occur from application of
an EUP as well as registered products,
which, if reported, would be essential to
making a well informed finding.
Registrants are reminded that FIFRA
section 6(a)(2) requires the submission
of such information for registered
products (see 40CFR part 159).
b. Product use information. EPA is
proposing to require (R) product use
information (guideline 875.1700) to
provide information on how the
pesticide is used and applied per day.
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Data would at least include: Typical
application methods, typical values for
application rates, timing and number of
applications per season or per year, any
available surveys that provide use
information for insect repellents, and
other use information relevant to
potential exposure following a repellent
application. Such use information
enables the Agency to appropriately
trigger other conditional data
requirements, i.e., identification of
potential exposure (risk), and conduct
more accurate and realistic risk
assessments, thus enabling the Agency
to levy appropriate limitations on use to
mitigate any potential risks. This data
requirement is newly codified since this
information is already submitted with
the label and the Agency could not
complete a risk determination (estimate
exposure) without the information.
c. Test note revisions and other
conditions exempting data. The Agency
is proposing to add the following
conditions at the onset to Tier I, Tier II,
and Tier III Human Health Assessment
Data Tables: Straight chain
Lepidopteran pheromones are exempt if
applied at a rate less than or equal to
150 grams active ingredient/per acre/
year (Ref. 15). EPA is no longer
requiring these data for SCLPs because
the past 20 years of scientific literature
supports waiving the data. SCLP’s do
not pose a risk to human health when
applied at a rate not to exceed 150
grams active ingredient per acre. This is
consistent with current implementation,
e.g., § 180.1124 requirements.
The Agency proposes to provide a test
note identifying when certain data are
required (acute oral, acute dermal,
primary dermal irritation), unless the
test material is a gas or highly volatile
(vapor pressure >104 torr). The current
data tables do not specify the trigger for
vapor pressure. Thus, the proposed rule
provides criteria and clarity.
iii. Revisions to existing
requirements—a. Primary eye irritation
and primary dermal irritation. The
Agency currently requires (R) these data
for MP or EP. The Agency is proposing
to require (R) these data for TGAI and
MP test substances since effects may
result from active ingredient or other
(inert) ingredients in the end-use
product.
b. Dermal sensitization. The Agency
conditionally requires (CR)
‘‘Hypersensitivity study’’ (152–15) in
current § 158.690. EPA proposes to
substitute dermal sensitization data
(guideline 870.2600) and to require (R)
the data, since the dermal sensitization
guideline measures the same endpoints
and more accurately describes the
nature of the type of data required in
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that it identifies dermal sensitivity. The
Agency considers this information a
method for accurately classifying the
dermal sensitization potential of the
pesticide and for determining whether
any observed adverse effects are
inherent to the active ingredient, or
caused by the presence of other
ingredients. In addition, the Agency
currently requires (R) this data for MP
or EP. The Agency is proposing to
require (R) this data for TGAI and MP
test substances since effects may result
from active ingredient or other (inert)
ingredients in the end-use product.
c. Mutagenicity. The Agency proposes
to change the name of the battery of
studies from ‘‘Studies to detect
genotoxicity’’ (152–17) to specific
mutagenicity studies including the
following: Bacterial Reverse Mutation
Test (guideline 870.5100), In vitro
Mammalian Cell Gene Mutation Test
(guideline 870.5300), and In-vivo
Cytogenetics (guideline 870.5385 and
870.5395) (Mammalian Bone Marrow
Chromosomal Aberration Test and
Mammalian Erythrocyte Micronucleus
Test, respectively). The Agency
proposes to split existing genotoxicity
data requirement (152–17) into four
different data requirements. The
following are proposed as Tier I
requirements: Bacterial Reverse
Mutagenicity (guideline 870.5100) and
In vitro Mammalian Cell Gene Mutation
TEst (guideline 870.5300) are proposed
to be required (R) for food uses and
conditionally required (CR) for nonfood
uses. The following are proposed Tier II
requirements: In vivo Cytogenetics
(guideline 870.5385 and 870.5395).
Second, the proposed Tier II studies,
mammalian spermatagonial
chromosomal aberration and
mammalian bone marrow chromosomal
aberration (guideline 870.5385 and
870.5395), are conditionally required
(CR) for food uses if Tier I data indicate
mutagenicity. The Agency is proposing
these organizational changes because
the original genotoxicity data
requirement was actually composed of
multiple studies and the actual data
requirements are more clearly described
when separated as found in today’s
proposal. For example, the current Tier
II data is required on mammals and
would be unnecessary if the Tier I data
shows no mutagenicity concerns. In
addition, the guideline under which the
old genotoxicity data requirement
references is 152–17 in the 1982
guidelines and it says ‘‘Data derived
from short-term microbial mutagenicity
tests are required...’’ and it mentions
gene mutations, structural chromosomal
aberrations, and direct DNA damage and
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repair (Ref. 9). The Agency designates
these as mutagenicity tests today and
the overall way the Agency
cumulatively test for mutagenicity has
evolved since then.
d. Prenatal developmental toxicity.
The Agency proposes to change the
name of this requirement from
‘‘Teratogenicity’’ to ‘‘Prenatal
developmental toxicity’’ to better
correspond with the focus of the study
and current terminology. The Agency
currently conditionally requires (CR)
this study for Tier I. The Agency
proposes to require (R) this study for
Tier I for food uses since food use has
the highest potential exposure to
humans during pregnancy; this
guideline will provide sound data if
needed to address prenatal
development. EPA encourages
preregistration meetings to determine if
the data requirement can be waived
because of minimal exposure; or
existing data on the product in the
scientific literature indicating there is
not a concern for developmental
toxicity. EPA will continue to
conditionally require (CR) these data for
a nonfood use. EPA is also proposing to
conditionally require (CR) these data on
a second test species for food and
nonfood uses as a Tier II data
requirement based on the condition that
there are reproductive effects (e.g.,
fetotoxicity, retarded development,
structural abnormalities, behavioral
abnormalities and/or death) evident in
Tier I, Prenatal Developmental Toxicity
(guideline 870.3700).
The Agency currently does not
require a reproduction study as Tier III,
and EPA is proposing to conditionally
require (CR) a reproduction and fertility
data requirement as a Tier III study
depending on the results of the Tier I
and II data requirements (i.e. subchronic
toxicity, prenatal development,
mutagenicity studies) in order to
address potential risks that may be
identified in lower tier studies.
In summary, for biochemical
pesticides, the tiered principle of testing
requirements for developmental toxicity
is as follows: identify the hazard
potential in Tier I for one species; if that
study is positive, another study is
required (2nd species) for use in
reducing the uncertainties of species-tospecies extrapolation (Tier II). If positive
mutagenicity or effects on reproductive
organs are observed in subchronic (Tier
II) studies, then the reproduction study
(Tier III) would be required for greater
certainty in risk characterization.
e. Immunotoxicity. The Agency
currently requires (R) Immune Response
data (152–18). The Agency has renamed
the guideline name and number to
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Immunotoxicity (guideline 880.3550)
and is proposing to conditionally
require (CR) such data as part of Tier II,
with a test note indicating this data is
required if there are effects on
hematology, clinical chemistry,
lymphoid organ weights and
histopathology observed in the 90–day
studies, or if the results of the Tier I
mutagenicity tests are positive. The
proposed change would make it
consistent with current evaluation
process for determining if a pesticide is
expected to pose immunotoxicity. This
is consistent with the Office of Pesticide
Programs historic waiver of this
requirement for SCLP’s, as well as when
there are no effects on hematology,
clinical chemistry, lymphoid organ
weights, etc. or when there is no
evidence of mutagencity concerns in
Tier I data.
The Immunotoxicity study (guideline
880.3550) provides information on
health hazards likely to arise from
subchronic exposure to a pesticide,
usually after dosing by the oral route
(emphasis added). Tests are selected to
provide quantitative and qualitative
data on the capacity of a pesticide to
adversely affect components of
antibody-mediated and specific and
non-specific cell-mediated immunity.
This purpose suggests that the oral route
is preferred, but the conditions for
requiring immunotoxicity testing
indicate that any route that is relevant
to each pesticide’s use pattern (primary
route of exposure under conditions of
use) is acceptable. (Results from one
insect repellent study that was done by
the dermal route p-menthane-3,8-diol
(Ref. 16) did not show any effects on the
immune system.)
EPA is also proposing to rename and
move a Tier II immune response data
requirement (152–24) to a Tier III data
requirement (immune response
guideline 880.3800). The Agency
proposes to continue to conditionally
require (CR) these data depending on
the results of the study completed to
satisfy the Tier II Immunotoxicity data
requirement. The Agency believes these
data address the endpoints more
suitably then the results found in the
Immune Response Study.
In summary, the Agency decided to
raise the level of tiers for the required
immunotoxicity data from Tier I to II
and from Tier II to Tier III, based on the
triggers used to require the
immunotoxicity data. In other words,
the results of the 90 day studies
requested under Tier I may trigger Tier
II immunotoxicity studies, but the
Agency would not be able to make that
determination until the data from Tier I
was reviewed. This is different from
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what was proposed in conventional
pesticides (70 FR 12275, March 11,
2005), which requires the data (though
not the same guideline (conventional
pesticides requires guideline 870.7800)),
since it is proposed to be required as
Tier I. The Agency discussed the
variability, and decided for biochemical
pesticides, given their low risk, it was
appropriate to defer until the data in
Tier I are reviewed and determined if
there was a potential for adverse effects
to the immune system.
f. Carcinogenicity. The Agency
proposes to change the name of the
‘‘Oncogenicity study’’ to
‘‘Carcinogenicity study’’ (guideline
870.4200) to reflect current terminology.
g. 90 Day–Oral Subchronic Testing.
The Agency currently conditionally
requires (CR) these data for food uses.
The Agency is proposing to require (R)
these data for food uses since people eat
food for periods longer than one day,
and since biochemicals have a non-toxic
modes of action, there is a need for
some data comparable to dietary
exposure to assure us that nothing
adverse is likely to happen when there
are higher than normal levels of the
biochemical in our food. For instance,
eating too much of a given vitamin can
be toxic or too much of an essential
element like iron can have some
unpleasant effects.
F. Nontarget Organisms and
Environmental Fate Data Requirements
1. General. The Agency uses a tiered
system of ecological effects and
environmental fate testing to assess the
potential exposure and risks of
pesticides to aquatic and terrestrial
vertebrates, invertebrates, and plants.
These tests include studies arranged in
a hierarchy from basic laboratory tests to
applied field tests. Laboratory tests
provide a screening tool for what can
potentially occur in the field, whereas
the field study data indicate the
potential adverse effects in the field.
The results of each tier are evaluated to
determine the potential impacts on fish,
wildlife and other nontarget organisms,
and to indicate whether further
laboratory and/or field studies (e.g., Tier
II, Tier III, and Tier IV) are needed. Tier
I ecological effects testing generally
consists of the basic data requirements
that are necessary to determine the
acute toxicity to nontarget fish,
invertebrate, plant, and wildlife species.
Tier II environmental fate data
requirements (there are no Tier I
environmental fate data requirements)
revolve around the characterization of
the pesticide in the environment, e.g.,
hydrolysis, soil and aquatic metabolism
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rate, photodegradation rate in soil and
water, etc.
Higher tiered studies may be
conditionally required when basic Tier
I data indicate there is potential for
adverse effects to nontarget species. Tier
II data requirements include an array of
environmental fate data requirements
and subchronic/chronic ecological
effects tests to further refine the
potential for exposure and/or risk to the
environment. Tier III data requirements
include a further array of field studies
that address ecotoxicity concerns for
terrestrial and aquatic animal species as
well as nontarget plants and insects.
These data provide a foundation for
ecological risk assessment, which
allows the Agency to determine any
appropriate precautionary statements or
mitigation measures necessary to
support registration concerning toxicity
or potential adverse effects to nontarget
organisms (including endangered
species).
With respect to some of the
environmental fate data requirements,
the Agency is providing two sets of
guideline numbers where needed, the
first guideline numbers are what are
currently used by the Agency. The
second set which are in (parentheses)
are guidelines the Agency has in draft
stage and hope to finalize in the near
future. To avoid confusion on the types
of data that are required, both numbers
are provided for each data requirement
as an interim measure until the
guidelines are finalized.
2. Nontarget organisms and
environmental fate data requirements.
The Agency is proposing to add the
redwing blackbird, Agelaius phoenicius,
to the list of species that may be
substituted for the other species (i.e.,
mallard or bobwhite quail). This test
species could be used for the avian oral
toxicity study because current data
requirements do not adequately
characterize the risks that pesticides
pose to songbirds. Other changes
include revisions in the test substance,
conditions under which the test is
conducted, and clarification of test
notes.
i. New data requirements. None.
ii. Newly codified data requirements.
a. Regulatory text revision. The current
part 158 for biochemicals does not
include regulatory text provisions
within the data table section discussing
the exemptions of data to support
arthropod pheromones
(§ 158.960(a)(2)).The Agency is
proposing the following language to be
part of the regulatory text in the
proposed rule:
(2) The data in this section (§ 158.960) are
not required for arthropod pheromones when
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applied at up to a maximum use rate of 150
grams active ingredient/acre/year except
when the product is expected to be available
to avian species (i.e. granular formulation).
It makes it clear from the onset under
what conditions these data are required.
Based on a survey of data and the
literature since 1984, EPA believes that
arthropod pheromones pose minimal
risk to nontarget species when applied
at this rate or less (Ref. 15). As a result
of this finding, EPA has historically
waived these data and is revising the
test note to reflect the current practice.
b. EP testing. Where nontarget and
environmental fate data are required,
the Agency currently requires (R) that
the TGAI be used as the test substance,
and does not generally require (R) or
conditionally require (CR) the EP to be
tested. EPA is proposing to
conditionally require (CR) EP testing
when any end-use formulation may
contain other ingredients that may be
toxic to nontarget organisms or to
support arthropod pheromones that
would be available to avian wildlife
(e.g., granular product).
c. Anerobic aquatic metabolism (162–
3 or guideline 835.4400) and anerobic
soil metabolism (162–2 or guideline
835.4200), are currently not required
(NR). The Agency is proposing to
conditionally require (CR) anerobic soil
metabolism for terrestrial use and
anerobic aquatic metabolism for both
terrestrial and aquatic uses. The Agency
believes that anerobic aquatic
metabolism is necessary if the pesticide
is intended for application to standing
water and/or low oxygen environments,
e.g., rice paddies, cranberry bogs,
wetlands in natural areas and would
already be required under these
circumstances under typical registration
practices for biochemicals.
iii. Revisions to existing requirements.
The Agency is proposing a reduction or
clarification in following five data
requirements: avian oral, avian dietary,
freshwater fish, freshwater invertebrate,
and plant toxicity testing. The Agency is
proposing to not require (NR) these
studies for terrestrial uses of arthropod
pheromones as defined in § 158.900.
Other proposed changes are as follows:
a. Avian acute oral (guideline
850.2100)—Redwing Blackbird. Part 158
currently only offers two test species for
testing, mallard and the bobwhite quail.
The Agency is proposing revisions to
the Avian Acute Oral data requirement,
specifically to add an optional test
species (i.e. redwing blackbird), in order
to address potential exposure to
passerine species in a terrestrial
environment. In addition, the Agency is
proposing to conditionally require (CR)
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EP testing if the formulation would be
available to avian wildlife, e.g., granular
formulation. Testing on a passerine
species (i.e., redwing blackbird) may be
required (R) for outdoor uses if the use
pattern lends itself to higher exposure to
passerine species compared to upland
game or waterfowl species. EPA is
requesting comments on whether this
species should replace the existing
bobwhite/mallard species for a
biochemical pesticide, or otherwise be
presented as an optional species for the
conduct of the test. If so, comments are
also sought on the specific criteria to be
used to determine when the testing on
this particular species would be
required.
In addition, the Agency is proposing
to conditionally require (CR) EP testing
when the following apply: when any
end-use formulation may contain other
ingredients that may be toxic to
nontarget organisms or when the enduse formulation is used to support
arthropod pheromones that would be
available to avian wildlife (e.g., granular
product).
b. Avian dietary (guideline 850.2200).
Part 158 currently requires (R) TGAI
testing for this data requirement. In
addition, the Agency is proposing to
conditionally require (CR) EP testing
when the following apply: when any
end-use formulation may contain other
ingredients that may be toxic to
nontarget organisms or when the enduse formulation is used to support
arthropod pheromones that would be
available to avian wildlife (i.e., granular
product).
c. Fish acute toxicity test (freshwater)
(guideline 850.1075), aquatic
invertebrate acute toxicity
(freshwater)test (guideline 850.1010).
The Agency currently requires (R) these
data for all terrestrial, aquatic, forestry,
and domestic outdoor uses. The Agency
conditionally requires (CR) the data for
greenhouse and indoor use. The Agency
proposes to add two test notes to the
current standards. The first proposed
test note indicates when EP data are
conditionally required (CR), the second
test note does not require testing for
compounds which are highly volatile.
d. Seedling emergence (guideline
850.4100) and vegetative vigor
(guideline 850.4250). Part 158 currently
requires (R) these data as Nontarget
Plant Toxicity testing to support
terrestrial and aquatic nonfood uses and
forestry uses. The Agency proposes to
require (R) these data for all outdoor
uses. Currently there is one test note
with three conditions identifying when
these data are required. The Agency is
proposing to eliminate these test note
conditions, but add a test note requiring
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EP testing when the end-use
formulation may contain other
ingredients that may be toxic to
nontarget plants.
e. Nontarget insect testing (guideline
880.4350). Currently the Agency
conditionally requires (CR) nontarget
insect testing (154–11) data with two
test note conditions. The Agency
proposes to be more transparent and
require (R) these data, for all uses except
indoor use. This is because it has
become apparent to the Agency
throughout the years, that is appropriate
to require insect testing especially with
these types of biochemical pesticides, to
ensure they are insect specific. In
addition, the actual test guideline
recommends that the guideline
850.3020 be conducted on the honeybee
initially, but that additional nontarget
insect species may be required. The
honeybee study is required since that is
what has been typically submitted and
addresses the issues for risk assessments
for biochemical pesticides.
f. Sediment and soil adsorption/
desorption for parent and degradates;
161–1 or guideline 835.1230, and soil
column leaching ( 163–1 or guideline
835.1240) currently designated as
adsorption-desorption. These data are
currently not required (NR) for
greenhouse use. Hydrolysis (161–1 or
guideline 835.2120) and Aerobic
Aquatic Metabolism (162–4 or guideline
835.4300) are also not required (NR) for
greenhouse use. The Agency is
proposing to conditionally require (CR)
these data for greenhouse use. The
proposed test note is also revised to
indicate all these data are conditionally
required (CR) depending on the results
of any of the Tier I data, not limited to
environmental fate data, since it is the
experience of the Agency that there may
be other indicators other than exposure
data which would trigger the need for
these data.
g. Laboratory volatilization from soil
(163–2 or guideline 835.1410)
designated as volatility in current data
requirements, and Aerobic soil
metabolism, 161–1 or guideline
835.4100. The Agency currently
conditionally requires (CR) these data to
support aquatic uses and do not require
(NR) these data to support greenhouse
use. The Agency is proposing to not
require (NR) these data to support
aquatic uses, and to conditionally
require (CR) these data to support
greenhouse use. Since the exposure is in
the soil, it is appropriate not to require
data in the water/sediment and it is
appropriate to require these data for
land type use. In other words, this
revision is consistent with the purpose
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and implementation, as well as with the
guidelines.
h. Photodegradation on soil (161–3 or
guideline 835.2410) and
photodegradation in water (161–2 or
guideline 835.2240) identified as Soil
photolysis and Aquatic photolysis in
current guidelines. Part 158 currently
conditionally requires (CR) these data
for all uses except greenhouse and
indoor use. That study is designed to
measure photolysis of a pesticide on the
surface of the soil. Water will attenuate
the amount of sunlight reaching
underlying sediments in a water body,
thereby making photolysis of a sediment
bound pesticide unlikely. In that case,
measuring photolysis of the pesticide in
the water column would be more
appropriate. Therefore, the Agency
proposes to not require (NR)
photodegradation of parent and
degradates in soil for aquatic (food and
nonfood), since photodegradation
cannot be measured in the soil under
the water, but the Agency is continuing
to conditionally require (CR) the direct
photolysis rate of parent and degradates
in water, since photolysis can be
measured. The Agency proposes to add
a condition for terrestrial, greenhouse,
and forestry uses, when the results of
Tier I studies demonstrate a concern for
toxicity, and an evaluation of potential
exposure (environmental fate) is needed
to make a risk determination. EPA also
proposes to change the names of these
studies from ‘‘soil photolysis’’ to
‘‘photodegradation on soil’’ as
designated in (161–3 or guideline
835.2410) and from ‘‘aquatic
photolysis’’ to ‘‘photodegradation in
water’’ also identified as direct
photolysis rate of parent and degradates
in water (161–2 or guideline 835.2240).
In essence, the proposed data
requirements are in line with the
proposed use patterns, where the
exposure is eminent.
i. Partition coefficient (n-octanol/
water) (guidelines 830.7550, 830.7560,
and 830.7570). Part 158 currently
conditionally requires (CR) this study
when results from Tier1 tests indicate
environmental fate data are needed. The
Agency proposes to relocate this
requirement under the product
chemistry data requirements. As further
explained in that section of the
preamble, the study would no longer be
dependent on Tier I studies, but would
be conditionally required (CR) for
organic chemicals unless they dissociate
in water or are partially or completely
soluble in water.
j. UV/light absorption (guideline
830.7050). Part 158 currently
conditionally requires (CR) this study
for all uses except greenhouse (food and
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nonfood) and indoor use. As explained
elsewhere, the Agency proposes to
transfer this data requirement to product
chemistry data requirements and to
require (R) this for all as part of the basic
data in the characterization and
identification of a compound. This
information will be used in conjunction
with the ‘‘photodegradation in water’’
study to determine if photodegradation
is a possible route of dissipation in the
environment. In order for a pesticide to
undergo direct photolysis in the
environment, it must absorb energy in
the wavelength range emitted by
sunlight. The UV/visible light
absorption spectrum will indicate
whether or not the pesticide absorbs in
this range.
k. Dispenser-water leaching (guideline
880.4425). Part 158 currently does not
require (NR) this study to support
greenhouse uses and indoor use. The
proposed rule conditionally requires
(CR) this study for greenhouse use and
does not require (NR) for aquatic uses.
This proposed change brings the data
table in line with the guideline and only
require the data when the pesticide is
applied to land in a passive dispenser.
l. Terrestrial wildlife, aquatic animal,
nontarget plant, and insect testing. The
Agency currently divides Tier III studies
into four categories: terrestrial, aquatic
animal, nontarget plant, and nontarget
insect testing. The Agency proposes to
identify individual studies and their
respective guideline numbers that may
be conditionally required (CR) when
results from lower tiered data indicate
the potential need for additional
studies. The test notes have not been
revised, therefore the conditions under
which these data are required will not
be revised. However, the Agency is
updating the guideline numbers. As a
result guideline 850.2300 through
850.2500 apply to various terrestrial
data requirements (avian and mammal),
guideline 850.1025 through 850.1500 for
aquatic animal data requirements
(freshwater and marine fish and
invertebrate species), and guideline
850.4225 through 850.4450 for nontarget
plant studies.
The Agency currently conditionally
(CR) requires Tier III nontarget insect
testing depending on the results of the
lowered testing for nontarget insects.
The Agency proposes to conditionally
require (CR) field pollinator testing (to
address risks to bees) data (guideline
850.3040) as Tier III, if the product is
expected to be transported during
application to air, soil, or water, which
is determined in the Tier II
environmental fate studies. Based on
industry information, and fate data
indication potential for exposure, we
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might then require some type of Tier III
testing. This testing would have to be
preceded by consultation with OPP,
because it would be directed at the
problem identified earlier. We would
need to consider the species at risk,
route of exposure, etc. Additional insect
species may have to be tested if
necessary to address issues raised by
use patterns and potential exposure of
important insect species, e.g., beneficial
insects, endangered species. The
guideline number is guideline 850.4030.
m. Product performance. Currently
the Agency relies on § 158.640 for
product performance data requirements
for biochemicals and microbial
pesticides. The Agency is proposing to
include product performance in the
regulatory text for both biochemicals
and microbial pesticides to improve
transparency. Product performance
verification can be important, especially
for public health pests, for some of the
biochemical and microbial pesticides
since we have seen independent reports
that some do not work as well as the
conventional pesticide products.
VIII. Microbial Pesticides Data
Requirements (Subpart M)
A. Definition of Microbial Pesticide
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Amendment to part 158. The Agency
is proposing a revision in the definition
of a microbial pesticide. The current
definition at § 158.65 of microbial
pesticides is:
Biochemical and microbial pesticides
are generally distinguished from
conventional pesticides by their unique
modes of action, low use volume, target
species specificity or natural
occurrence. In addition, microbial
pesticides are living entities capable of
survival, growth reproduction and
infection. ... Microbial pesticides
include microbial entities such as
bacteria, fungi, viruses, and protozoans.
The data requirements apply to all
microbial pesticides, including those
that are naturally-occurring as well as
those that are genetically modified. Each
‘‘new’’ variety of subspecies, or strain of
an already registered microbial pest
control agent must be evaluated, and
may be subject to additional data
requirements.
The definition of a microbial pesticide
in the proposed rule is as follows:
Microbial pesticide means a
microorganism intended for preventing,
destroying, repelling, or mitigating any pest,
or intended for use as a plant regulator,
defoliant, or desiccant, that: (1) Is a
eucaryotic microorganism including, but not
limited to, protozoa, algae, and fungi; (2) Is
a procaryotic microorganism, including, but
not limited to, bacteria; or (3) Is an
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autonomous replicating microscopic element,
including, but not limited to, viruses.
B. Applicability of Microbial Pesticide
Data Tables
This proposed definition of microbial
pesticide is based on the language in the
current definition of microbial pesticide
at § 158.65 and the class of nonexempt
biological control agents in
§ 152.20(a)(2), but uses a structure for
defining microbial pesticide similar to
that at 40 CFR 172.43. Specifically, the
proposed definition replicates the
structure used in § 172.43 that identifies
the intent of the microbial pesticide, for
example, as the prevention or
destruction of a pest. The proposed
definition also combines the structure
and examples at § 152.20 with the
current regulatory structure to clarify
the intended scope of the current
regulatory definition and relationship to
§ 152.20. For example, the proposed
definition includes references to
eucaryotic and procaryotic
microorganisms, terms not found in the
current definition at § 158.65 but found
in § 152.20(a)(3). The proposed
definition also clarifies that microbial
pesticides include viruses and other
similar infective elements, while the
’’autonomous replicating‘‘ language is
intended to exclude pesticide
components of microscopic cells that
are not able to replicate as separate
entities, such as genetic constructs
inserted intentionally into the cells.
None of these proposed amendments are
intended to change the scope of the
current regulatory definitions of
microbial pesticide at § 158.65 or of the
exemption provision at § 152.20(a)(3).
EPA is also proposing not to include
in the definition of microbial pesticide
the phrase from current § 158.65
distinguishing microbial pesticides from
conventional pesticides because the
original definition was more of a
description of those characteristics that
might be shared by both biochemical
pesticides and microbial pesticides. In
this rule, we have described
biochemical pesticides separately and
we can now be more specific in defining
microbial pesticides.
EPA notes that microorganisms are
known to produce many pesticidal
substances. These pesticidal substances,
when used independently of the
microorganism, are considered to be
biochemical pesticides, conventional
chemical pesticides, or antimicrobial
pesticides, depending on the mode of
action and the use. The microorganism
would then usually be considered part
of the manufacturing process. For
example, streptomycin, an antibiotic
produced by a bacterium, Streptomyces
griseus, is registered as a conventional
chemical fungicide.
EPA is proposing to create a new
applicability provision expressly
providing that the microbial pesticide
data tables apply to microbial
pesticides, as described previously, and
to add to that paragraph specifics on the
types of microbials subject to the
subpart M data requirements.
First, the language in current § 158.65
states that ‘‘each new variety of
subspecies, or strain of an already
registered microbial pest control agent
must be evaluated, and may be subject
to additional data requirements.’’ The
proposed refinement now reads ‘‘each
new isolate of a microbial pesticide is
treated as a new strain and must be
registered independently of any similar
registered microbial pesticide strain and
supported by data required in this
subpart.’’ This refinement is simply
intended to clarify the intent of the
current regulatory language.
The second sentence added to the
applicability provision states that
genetically modified microbial
pesticides may be subject to additional
data or information requirements on a
case-by-case basis depending on the
particular microorganism and/or its
parent microorganism(s), the proposed
pesticide use pattern, and the manner
and extent to which the organism has
been genetically modified. That
language is moved from current
§ 158.65.
The final sentence reads ‘‘pest control
organisms such as insect predators,
nematodes, and macroscopic parasites
are exempt from the requirements of
FIFRA as authorized by section 25 (b) of
FIFRA and specified in § 152.20 (a) of
this chapter.’’ That sentence is moved
from current § 158.65 as well.
In addition, the current regulatory text
at § 158.65 specifies that the microbial
‘‘data requirements apply to all
microbial pesticides, including those
that are naturally-occurring as well as
those that are genetically modified.’’
This language is not needed in the
definition; the use of the data
requirements for microbial pesticides is
fully described in the section
immediately following the definition.
Other portions of the current text at
§ 158.65 are proposed to be moved to
the applicability subsection of subpart
M, § 158.1000, or the other provision
that seems generic § 158.1010 to avoid
confusion on the definition of microbial
pesticide. Specifically, EPA is proposing
to move current § 158.65(b)(2) to
proposed § 159.1010.
EPA is also proposing to use table
descriptors NR (not required), R
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(required), and CR (conditionally
required) to be used as markers along a
spectrum of the likelihood that a data
requirement applies. In other words, it
should be assumed that a required (R)
data requirement is required typically
all the time. There may be some narrow
or rare conditions identified in test
notes when data are not required. For
example, acute injection toxicity
(intraperitoneal or intravenous) not
required when the microbial pesticide is
a virus. In contrast, a conditionally
required (CR) data requirement is less
likely to be triggered compared to a
required (R) data requirement, but more
likely include test notes indicating
conditions when data are typically
required. For example, the primary
dermal irritation is currently
conditionally required (CR) for
microbial pesticides. The test note
indicates it is required (R) when dermal
irritation is reported from the acute
dermal toxicity study. Specific criteria
are identified with the test note.
C. Amendment of Part 172
The Agency is also proposing to
replace the definition for a microbial
pesticide at 40 CFR 172.43 with the
definition proposed here. The proposed
definition is broader than the definition
at § 172.43 in that it uses the term
‘‘includes’’ rather than ‘‘means’’ and
identifies a category for autonomous
replicating microscopic elements, rather
than just including viruses. EPA is
proposing a broader definition because
it has been EPA’s experience that there
are microorganisms other than viruses
that could be used as a pesticide but
that would otherwise be excluded by
the definition at § 172.43.
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D. Product Analysis Data Requirements
1. General. The Agency uses product
analysis information to determine
whether impurities of toxicological or
environmental concern are present in
the pesticide and formulated products.
Product analysis data requirements
include product identity and
composition data, physical and
chemical characteristics of a pesticide,
plus any intentionally added
ingredients and impurities in the final
pesticide product. Included in this
category are the specific, detailed
requirements for product identity and
chemical analysis. The title of the data
requirements, ‘‘microbial pesticides
product chemistry data requirements,’’
is proposed to be revised to ‘‘microbial
pesticides product analysis data
requirements’’ to better reflect the extra
identification procedures necessary to
analyze living organisms. The following
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discussion addresses the proposed data
requirements.
2. Product analysis data requirements.
Currently, the Agency groups all the
physical and chemical properties
studies under one section. The Agency
proposes instead to list the individual
studies that are included in the category
of data requirements to support
registration (guideline 830.6302 through
830.7300). The Agency currently
requires (R) all product chemistry data
to support registration, except for
analysis of samples and submittal of
samples, which is proposed to be
required under residue chemistry data
requirements.
i. New requirements. None.
ii. Newly codified requirements.
None.
iii. Revisions to existing requirements.
a. Product identity, manufacturing
process, and deposition of a sample in
a nationally recognized culture
collection. Currently these data are
required as guideline numbers 151–20,
151–21, and 151–22. The Agency
proposes that these data requirements
would remain the same as before.
However, we are proposing to list each
as a separate study: product identity;
manufacturing process; and, discussion
of formation of unintentional
ingredients. The Agency proposes to list
them as follows: product identity
(guideline 885.1100), manufacturing
process and deposition of a sample in a
nationally recognized culture collection
(guideline 885.1200), and discussion of
formation of unintentional ingredients
(guideline 885.1300).
b. Physical and chemical
characteristics. The Agency currently
requires (R) physical and chemical
characteristics data. The Agency
proposes to require (R) that the same
studies and same endpoints be
evaluated, however the Agency is trying
to be more clear by identifying the
individual pieces of the data
requirement and separately identify
each in the data table. Specifically the
studies are identified as: color, physical
state, odor, stability, storage stability,
miscibility, corrosion characteristics,
pH, viscosity, and density (guidelines
830.6302 through 870.7300).
c. Analysis of samples. This study
(guideline 885.1400) is currently
conditionally required (CR) for EUPs
and registrations. The Agency proposes
to revise this data requirement to be
required (R), since it is critical to have
an analysis of samples to understand the
composition of the microbial pesticide
and the potential for contamination
with other microorganisms.
d. Certification of limits. This study is
currently required (R) except for
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nonfood uses. The Agency is proposing
to expand this data requirement to be
required (R) for all uses. These studies
are needed to confirm the claims made
on the label and to validate the
confidential statement of formula.
e. Analytical methods. The analytical
methods would typically assure that
you could quantify the confidential
statement of formula. This study is
currently required (R), and the Agency
proposes to continue to require (R) these
data, but under product identity and
discussion of unintentional ingredients
data requirements, which provide these
data.
f. Submittal of samples. This
provision is typically intended to enable
EPA to identify the active ingredient
and provide standards to governmental
agencies needing to monitor chemical
pesticide residues and is conditionally
required (CR). The Agency proposes to
require (R) these data as a product
analysis requirement to be deposited in
a nationally recognized culture
collection to allow EPA to validate
strain identity if issues arise (guideline
885.1200).
Since the Agency does not have
capacity to store the variety of microbial
pesticides that may be submitted, EPA
did not set up a nationally recognized
culture collection. There are several
nationally recognized culture
collections in this country (and abroad)
such as the American Type Culture
Collection and a microbial collection
maintained in Peoria, Ill., by the USDA.
These facilities have a vast number of
microbial and cell cultures that are
dedicated to transferring, maintaining
and identifying. Rather than duplicate
this effort, EPA chose to refer microbial
pesticide producers to these facilities
who have the routine expertise to keep
and distribute (or protect) microbial
cultures. There is a certain element of
required expertise but really the cost
and small number of our microbial
pesticides would make it prohibitively
expensive for the Agency to do this
collection rather than direct the
companies to these specialized
facilities.
E. Residue Chemistry Data
Requirements
1. General. The Agency uses residue
chemistry information to determine the
potential bioavailability of pesticide
residues on food. Included in this
subpart are the detailed requirements
for chemical identity, analytical
methods for plants and animals, nature
of residue, stability, and magnitude of
residue.
2. Residue chemistry data
requirements. The residue chemistry
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data table currently requires residue
data under one data requirement. The
Agency is proposing to delineate the
residue data to clearly identify the
endpoints being measured. In other
words, there is only one data
requirement, and in the proposed rule
there are several data requirements
listed (guideline 885.2000 through
885.2350), but no more additional data
are actually required. In addition, the
current test note in part 158 delays the
residue study requirement until
Toxicology Tier II and Tier III data are
required (R). The Agency is proposing
the data requirement not be dependent
on the Tier Data in II and III, but to
conditionally require (CR) these data
when the results of testing (indicated in
test note).
i. New requirements. None.
ii. Newly codified requirements.
None.
iii. Revisions to existing requirements.
Part 158 currently requires residue data
(153–4) for microbial pesticides, but
does not lay out clearly the various
underlying studies for fulfilling the
actual requirement. EPA proposes the
following be listed to provide greater
clarity and transparency of the data that
are actually required (R) to support
registration: Background for residue
analysis of microbial pest control agents
(guideline 885.2000), chemical identity
(guideline 885.2100), nature of residue
(guideline 885.2200, 885.2250),
analytical methods (guideline
885.2300,885.2350), storage stability,
magnitude of residue (guideline
885.2500, 885.2550, 885.2600). These
data are currently required (R), therefore
there is no revision in the proposed
rule.
F. Toxicology Data Requirements
1. General. Toxicology data
requirements encompass studies
expected to improve the Agency’s
understanding of the potential pesticide
hazard to humans, including
subpopulations such as infants and
children, and domestic animals, for all
microbial pesticides. These data
requirements include acute toxicity/
infectivity studies (oral, dermal,
inhalation, pulmonary injection), a cell
culture study, and hypersensitivity
incidents (guideline 885.3050 through
885.3500) to be submitted. In addition,
acute toxicity studies (oral, dermal, and
inhalation) and the primary eye and
dermal irritation studies (guidelines
870.1100 through 870.2500) are also
required. The Agency wants to specially
note that we are inviting public
comment as to whether or not
hypersensitivity incidents (guideline
885.4300) is addressed adequately via
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the § 152.125, FIFRA section 6 (a)(2)
data requirement, also discussed in the
preamble for biochemical pesticides.
The following identifies the revisions
to the current § 158.740 for microbial
toxicology data requirements. Revisions
include name changes, test note
clarifications, revisions under which
use pattern data are triggered (e.g., food
use versus non-food use), and
clarification of other circumstances
under which data are required.
2. Toxicology data requirements. The
Agency generally discourages a
registrant from pursuing registration of
a microbial pesticide that is a known
human pathogen, even one reported to
be an opportunistic human pathogen,
because it would be difficult to support
a risk assessment that would show no
unreasonable risk to humans. However,
in some cases, a candidate microbial
pesticide may:
(a) Be very closely related to a human
pathogen but lack the toxins or invasive
factors responsible for that disease;
(b) Be taxonomically distinct from
known human pathogens, but may have
picked up a toxin or other factor that
could cause mammalian disease as
detected by Tier I and II studies; or,
(c) Provide significant benefits that
would offset some risk that might
additionally be mitigated by certain use/
exposure considerations.
The Agency has encountered several
cases where microbial pesticides are a
member of a taxonomic group
containing mammalian toxins. In these
instances, data gathering beyond the
codified data requirements may be
required to account for potential human
health risks. For most applications, this
kind of testing is not needed.
Generally, toxicology data from Tier I
is sufficient to address the hazards
related to the human health risk
assessment for pathogenicity and
infectivity of microbial pesticides. The
most common reason for needing Tier II
or higher tests is the appearance of
unexplained toxicity, unusual
persistence, lethality, or adverse effects
related to treatment with the microbial
pesticide in the Tier I studies.
Some microbial products may be
lethal to rodents at the Tier I and/or Tier
II levels, where the mode of action may
not be sufficiently clear to allow for
specific toxin or other infectivity factors
to be analyzed. Furthermore, due to the
nature of some microorganisms, the
possibility exists that rodents may not
be a truly representative test animal for
determining effects on humans of a
microbial pesticide.
The Agency proposes to conditionally
require (CR) Infectivity/ pathogenicity
as a Tier III data requirement. This
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requirement allows for the possible use
of alternative test species, including
primates as described in the testing
guidelines.
In addition, there are ten revisions,
primarily name changes to the data
requirements.
i. New requirements—Infectivity/
pathogenicity. Currently this study is
not required. The Agency is proposing
to conditionally require (CR) a Tier III
infectivity/pathogenicity analysis
(guideline 885.3000) when the microbial
pesticide appears to be a mammalian
pathogen that might sufficiently affect
humans or nontarget mammals. While it
is possible that the registrant would not
want to pursue a microbial registration
if such testing were triggered, the
Agency believe it is appropriate to
establish a Tier III toxicity study
requirement to evaluate the microbial
pesticides potential effects in higher
animals. The Agency believes this type
of data would rarely be required.
However, if all criteria established in
the revised test notes has been
exceeded, it is appropriate to require the
data.
ii. Newly codified requirements.
None.
iii. Revisions to existing
requirements— a. Acute oral toxicity/
pathogenicity. Currently this study is
required (R) with no test notes. For
clarity, the Agency is proposing a name
change to the more descriptive one used
in the updated guidelines (guideline
885.3050). EPA also proposes a
reduction in the number of test
substances required to be tested.
Currently, part 158 requires both MP or
EP and TGAI. The proposed rule would
only require (R) the TGAI to be tested.
TGAI is only required for the acute oral
toxicity/pathogenicity and can be done
with MP or EP to avoid the ‘‘normal’’
acute oral toxicity for the EP if all
endpoints and dosing are confirmed.
The endpoint examined in the toxicity/
pathogenicity include clearance and
immune functioning of the test rodent.
These endpoints, once determined, are
not necessary for more than the TGAI.
The MP and the EP are not expected to
dramatically alter the pathogenicity
character of the microbe so the extra
testing does not add to the safety
assessment. The Agency is also
proposing to add a test note, indicating
the acute oral study toxicity/
pathogenicity can be combined with the
unit dose portion of acute oral toxicity
study (guideline 870.1100) if the new
protocol is designed to address the
endpoints of concern.
b. Acute pulmonary toxicity/
pathogenicity. The Agency currently
requires (R) the acute inhalation study
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(152–31) under Tier I. The Agency is
proposing acute pulmonary toxicity/
pathogenicity (guideline 885.3150) to be
required in lieu of the acute inhalation
study. EPA also proposes a reduction in
number of test substances required to be
tested, currently both MP or EP and
TGAI are required. The proposed rule
would only require (R) the TGAI to be
tested. These endpoints, once
determined, are not needed for more
than the TGAI. As discussed previously,
the MP and the EP are not expected to
dramatically alter the pathogenicity
character of the microbe so the extra
testing does not add to the safety
assessment.
c. Acute injection toxicity/
pathogenicity (Intravenous or
Intraperitoneal). The Agency currently
requires (R) I.V., I.C., I.P. injection
study. The Agency is proposing acute
injection toxicity/pathogenicity (either
intraperitoneal or intravenous) to also
be required (R), with the test note
indicating the pathway under what
conditions the intravenous or
intraperitoneal would be required.
Intracerebral is no longer required since
it has been determined that exposure
would most likely result in intravenous
or intraperitoneal exposure. Under this
revised data requirement, the data
would not be required if the active
ingredient of the pesticide product is a
virus.
d. Primary dermal irritation. The
Agency currently requires (R) this data
under Tier I. The Agency is proposing
to conditionally require (CR) these data
as Tier I, with proposed test notes better
defining the conditions when the data
requirement would apply. This study
would be conditionally required (CR)
only if dermal irritation was indicated
in the acute dermal toxicity study, since
it would be evident in the results of the
acute dermal toxicity study if primary
dermal toxicity effects could occur.
e. Acute inhalation toxicity. Currently
the Agency conditionally requires (CR)
an acute inhalation study (151–41) in
Tier II on MP or EP product when data
in a Tier I acute inhalation study
indicate potential adverse effects (e.g.,
survival, replication, infectivity,
toxicity). The Agency is proposing to
require (R) the acute inhalation toxicity
study (guideline 870.1300) as a Tier I,
limiting it to testing MP or EP, no longer
requiring TGAI testing, but with a test
note indicating data are required only if
the product can be inhaled.
f. Hypersensitivity study and
hypersensitivity incidents. Currently the
Agency requires (R) the hypersensitivity
study and conditionally requires (CR)
hypersensitivity incidents. The Agency
is proposing to not require (NR) the
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hypersensitivity study and to require (R)
hypersensitivity incident reporting data.
The hypersensitivity study are currently
submitted as part of product
characterization on known microbial
hazards such as toxins and allergens.
As indicated, the Agency proposes to
revise hypersensitivity incidents from
the current conditionally required (CR)
to proposed required (R), even under
conditions of EUP’s. While these types
of data are already required under
§ 152.125, FIFRA 6(a)(2), the status of
hypersensitivity incidents reporting is
unclear for microbial products that have
not been registered or are under an EUP.
Therefore, the Agency included a
requirement for hypersensitivity
incident reporting for EUP’s in lieu of
the hypersensitivity study. As
previously indicated, EPA is inviting
comment as to whether or not this study
is needed, since the data must already
be submitted to the Agency as 6(a)(2)
data.
g. Cell culture. The Agency proposes
to rename the currently required (R)
tissue culture study for all viruses to the
cell culture data requirement (guideline
885.3500), since this study is a more
appropriate name for the tissue culture
study and would only be required when
the product’s active ingredient is a
virus.
h. Reproductive fertility effects. The
Agency currently conditionally requires
(CR) teratogenicity data. The Agency is
proposing to conditionally require (CR)
reproductive and fertility effects data
(guideline 885.3650). This study
replaces both guidelines 152–47 and
152–53. This is actually a replacement,
since the data are basically assessing the
same endpoints. The Agency is also
proposing to not require these data as
Tier II, but as Tier III since the triggers
for this study rely on toxicity endpoints
which are collected in Tier II studies,
i.e., guideline 885.3600.
G. Nontarget Organisms and
Environmental Fate Data Requirements
1. General. The Agency uses a tiered
system of ecological effects testing to
assess the potential risks of pesticides to
nontarget aquatic and terrestrial
vertebrates, invertebrates, and plants.
These tests include studies arranged in
a hierarchy from basic laboratory tests to
applied field tests. The results of each
tier are evaluated to determine the
potential impacts on fish, wildlife, and
other nontarget organisms, and to
indicate whether further laboratory and/
or field studies are needed. These data
requirements provide the Agency with
ecological effects information, which, in
turn, allows the Agency to determine if
precautionary statements concerning
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toxicity or potential adverse effects to
nontarget organisms are necessary, or
whether the pesticide should be
registered for certain use patterns at all.
Higher tiered nontarget organisms and
environmental fate studies may be
required when basic human health
assessment data and predicted exposure
levels or environmental conditions
suggest the potential for adverse effects.
Field data are used to examine acute
and chronic adverse effects on captive
or monitored populations under natural
or near-natural environments. Such
studies would be required only when
the potential for adverse effects is
indicated by the results of lower tier
studies, or to confirm the need for
mitigation measures. In some cases, the
results of field studies may also give rise
to the need for further testing.
2. Nontarget organisms and
environmental fate data requirements.
The proposed nontarget organisms and
environmental fate data table reflects
the data that are currently required to
support registration of new microbials.
Conditions under which data may be
required are stipulated in the test notes.
In addition, there are a few studies that
would be replaced by more appropriate
studies to measure the endpoint of
concern, and other studies would be
deleted. These data revisions are not be
expected to substantively increase the
nature or burden of the existing data
requirements.
i. New requirements. None.
ii. Newly codified requirements.
None.
iii. Revisions to existing requirements.
a. Avian Inhalation Toxicity/
Pathogenicity. The Agency currently
requires (R) an avian injection test. The
Agency proposes to replace the avian
injection test (154–17) with the avian
inhalation test (guideline 885.4100) to
provide a more appropriate endpoint to
assess risks to avian species. The
Agency is also proposing to
conditionally require (CR) this data only
when the microbial pesticide appears to
have toxins that indicate potential
pathogenicity. The inhalation study
models a more realistic route of
exposure in the wild than
intraperitoneal injection.
b. Fish life-cycle study and aquatic
invertebrate range testing. The Agency
proposes to replace conditionally
required (CR) aquatic embryo larvae and
life cycle studies (154–28) with
conditionally required (CR) fish lifecycle studies (guideline 885.4700) and
definitive aquatic animal tests (154–27)
with aquatic invertebrate range testing
(guideline 885.4650) to provide more
appropriate endpoints for assessing
risks to aquatic species (fish and
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invertebrates). The ‘‘fish’’ life cycle
study is more appropriate because it
identifies a particular taxonomic class to
be tested as opposed to ‘‘aquatic embryo
and life cycle studies’’ which do not
identify the taxonomic class or species
to be tested. ‘‘Definitive aquatic animal
tests’’ does not say what animal group
(species) is to be tested and does not say
what test is to be done (‘‘definitive’’ is
not a test name), whereas ‘‘aquatic
invertebrate range testing’’ is more
appropriate because it specifically
instructs the registrant to determine
which aquatic invertebrate species are
susceptible to the pesticide and which
are not susceptible. In summary, the
Agency is proposing to revise the titles
of the data requirements in order to
account for species and life cycles being
tested.
c. Simulated or actual field testing for
plants (guideline 850.2500). The Agency
currently conditionally requires (CR)
nontarget plant studies (154–31) as Tier
III when data in Tier II indicate there is
a concern. The Agency proposes to
rename the data requirement to
simulated or actual field testing for
plants (guideline 850.2500), which is
currently conditionally required (CR) on
a case-by-case basis. The test notes
associated with the proposed
requirement are more explicit as to
when the conditions would be met. In
addition, these data are proposed to be
conditionally required (CR) as Tier IV.
d. Product performance. Currently the
Agency relies on § 158.640 for product
performance data requirements for
biochemicals and microbial pesticides.
The Agency is proposing to include
product performance in the regulatory
text for both biochemicals and microbial
pesticides to improve transparency.
Product performance verification can be
important for some of the biochemical
and microbial pesticides since we have
seen independent reports that some do
not work as well as the conventional
pesticide products. It is particularly
useful to have product performance data
for those products that want to be
considered as presenting less risk than
a conventional pesticide product.
e. Subchronic toxicity/pathogenicity.
The Agency proposes to change the
name of the subchronic oral toxicity
study (152–42) to correspond with the
current name of the test guideline.
f. Carcinogenicity. The Agency
proposes to change the name of the
oncogenicity study to carcinogenicity
study (guideline 870.4200) to
correspond with the current name of the
test guideline.
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IX. Peer Review
A. National Research Council
Recommendations
As discussed in Unit V.A.3, the
National Academy of Sciences issued a
report in 1993 entitled, ‘‘Pesticides in
the Diets of Infants and Children.’’ The
study, conducted by the National
Research Council, was initiated to
address the question of whether the
current regulatory system adequately
protected infants and children from
pesticide residues in food. The Council
reviewed current EPA practices and
data requirements related to dietary risk
assessment as well as testing
modifications planned by the Agency.
The panel of experts concluded that, at
that time, EPA approaches to data
requirements and risk assessments
emphasized the evaluation of the effects
of pesticides in mature animals and, in
general, there was a lack of data on
pesticide toxicity in developing
organisms. The Council also expressed
the need to investigate the effects of
pesticide exposure on immunotoxic
responses in infants and children (Ref.
3).
B. FIFRA Scientific Advisory Panel
1. 1994 SAP Review. In 1994, EPA
held a two day meeting of the SAP to
review the Agency’s proposed
amendments to the data requirements
for pesticide registrations contained in
40 CFR part 158. The SAP was asked to
comment on each data requirement and
identify, in their opinion, which ones
were necessary to fully and thoroughly
evaluate the potential hazard of a
chemical compound and which ones
were not intrinsically useful in
providing practical scientific
information. While these data
requirements were presented to SAP to
support conventional pesticides, the
majority of changes to the data
requirements presented in this notice
were submitted for review as subpart M:
Microbial and Biochemical Pesticides
Data Requirements. These revisions
were generally endorsed by the SAP
(Ref. 4). A copy of the 1994 SAP final
report can be found in the docket for
this rulemaking (docket ID number
EPA–HQ–OPP–2004–0415).
The limited issues that were
addressed in1994 Panel’s specific
comments are as follows:
• Intraperitoneal study. The issue
revolved around whether an
intraperitoneal study is appropriate to
use when microbial size or physical
properties preclude the use of
intravenous study. At that time, SAP
believed the intraperitoneal study was
appropriate to use when microbial size
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or physical properties preclude the use
of intravenous study. This option is
included in the proposed rule.
• Bird species. The issue revolved
around whether the second bird study
gives significant additional information
for microbial effects, i.e., are the two
birds species likely to respond
differently to typical biocontrol
microbials. At the time, SAP suggested
that it was appropriate to use only the
more sensitive bird species (the quail)
for data requirements. This
recommendation has been included in
the test note.
• Fish species. The issue revolved
around whether the second fish study
was likely to provide significant
information for microbials. At the time,
SAP suggested that it was appropriate to
use the more sensitive fish species
(trout) for data requirements. The SAP
recommendation was incorporated into
the test note.
Additionally, SAP encouraged the
Agency to carefully evaluate the data
requirements for genetically engineered
microbials. The SAP believed this
emerging technology was still, in many
respects, an unknown entity. In the
future, EPA will develop data
requirements for plant-incorporated
protectants.
2. 1987 SAP Review—Immunotoxicity
testing of biochemical pest control
agents (BPCAs) (Ref. 7). Proposed
Guidelines for Immunotoxicity Testing
of Biochemical Pest Control Agents
were presented to the SAP. In particular
the issues revolved around the use of a
single sex of test animal in the lower
tiered studies. At that time, the 1987
SAP decided that there was no scientific
rationale for examining both male and
female animals, though this may not
apply to compounds that demonstrate
estrogenic activity. In this case females
may be the sex of choice since they
would be more sensitive to
immunotoxic effects than males by this
class of compounds. A second issue
raised at this meeting was the inclusion
of a limit test in Tier I, in which no
adverse immunological effects are
observed at a single high dose, then no
further testing is required. The Agency
was seeking advice on the scientific
criteria that would support the
inclusion or exclusion of a limit test in
Tier I studies. At that time, the SAP
deemed it appropriate for all assays in
Tier I to be included since no single test
can fully evaluate all cellular or
functional components of the immune
system. A dose that produces a large
amount of general toxicity would be of
concern since the general toxicity might
indirectly contribute to the
immunotoxicity. Immunotoxicity data
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should be cautiously evaluated in this
context.
3. 1986 SAP Review—Applicator/user
exposure monitoring guidelines. The
Series 875, Group A, Applicator/User
Exposure Monitoring Guidelines were
presented to SAP in January 1986. After
EPA addressed SAP comments, the
guidelines were finalized. The
guidelines were published by the
National Technical Information Service
(NTIS) in 1987 (Ref. 10).
A comprehensive listing of data
requirements and the year that each
specific data requirement was reviewed
by SAP is available in the docket for this
proposed rule (Ref. 11). Additionally,
copies of documents reviewed by SAP
and the final reports can be found on
EPA’s website at https:// www.epa.gov/
scipoly/sap.
X. Animal Welfare Concerns
The Agency is committed to the
development and use of alternative
approaches to animal testing. The
Agency understands many people’s
concern about the use of animals for
research and data development
purposes. EPA has received comments
concerning the use of new and revised
test methods which would reduce the
number of test animals in studies, or
refine procedures to make them less
stressful to animals. The Agency
believes it has taken steps, based on
current scientific knowledge and
experience, to minimize testing on
biochemical and microbial pesticides.
With respect to these types of
pesticides, the Agency has implemented
a tiered testing approach, thereby
potentially reducing the number of
studies required for registration. Where
testing is needed to develop
scientifically adequate data, the Agency
is committed to reducing or replacing,
wherever possible, the number of
animals used for testing by
incorporating in vitro (non-animal) test
methods or other alternative approaches
that have been scientifically validated
and have received regulatory
acceptance. EPA considers these goals
and commitments to be important
considerations in developing health
effects data, consistent with the
essential need to conduct scientifically
sound pesticide hazard/risk assessments
in support of the Agency’s mission.
Taking into consideration principles
of sound science and the requirements
of FIFRA to protect humans (including
sensitive subpopulations) and the
environment from unreasonable
uncertainty of no harm from pesticide
exposure, the Agency is committed to
avoiding unnecessary or duplicative
animal testing. For example, currently
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EPA accepts data on the pH of a
pesticide as a screen to judge whether
the pesticide may be corrosive to the eye
or skin. Making this determination
avoids actual testing on animals. Many
long-term studies can be combined so
that several toxicological end-points can
be discerned from fewer studies. The
Agency already has bridging and
batching policies in place to allow the
use of acute toxicity, sensitization, or
irritation test data on products to be
used to support other products.
The Agency plays an important role
in the Federal Interagency Coordinating
Committee on the Validation of
Alternative Methods (ICCVAM) (https://
iccvam.niehs.nih.gov/home.htm).
ICCVAM, a standing committee made
up of 15 Federal agencies and
established through the National
Institute of Environmental Health
Sciences, which works to (1) encourage
the reduction of the number of animals
used in testing; (2) seek opportunities to
replace test methods requiring animals
with alternative test methods when
acceptable alternative methods are
available; and (3) refine existing test
methods to optimize animal use when
there is no substitute for animal testing.
ICCVAM convenes independent peer
review panels to evaluate specific
proposed test methods and has
developed consensus criteria for judging
the validation status of test methods.
Guideline 870.1100 references the use
of appropriate alternative test protocols
as a means of reducing the number of
animals used to evaluate acute effects of
pesticide exposure. Yet the Agency and
the scientific community also recognize
that test guidelines are designed to be
updated and supplemented frequently.
As new tests and test batteries are
validated, the Agency presents them to
the SAP. The Agency considers the
SAP’s determination of the reliability of
the test guidelines and their
applicability to meeting its regulatory
needs under FIFRA. After SAP review,
the Agency is planning to incorporate
validated in vitro screening data for skin
corrosion to its test guidelines. As other
appropriate alternative or in vitro
methods become available, they would
continue to be added to the test
guidelines.
XI. Data Requirements Specific to
Endangered Species Assessments and
Determinations
Over the last several years, the
Agency has been requiring, on a caseby-case basis for certain pesticides
(mostly conventional chemical
pesticides), data demonstrating specific
geographic location(s) of threatened and
endangered species (listed species),
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which can then be compared with areas
of potential pesticide use. These data
have been required when EPA
determined that the estimated
environmental concentration of the
pesticide when applied according to the
labeling appears to exceed the Agency’s
numeric concern levels for listed
species. The specific species for which
location information was needed, has
been determined on a case-by-case basis
based upon the use pattern of the
pesticide and the site on which it was
authorized to be used.
In general, a biochemical pesticide is
not expected to pose endangered species
concerns because it is a naturallyoccurring chemical or a syntheticallyderived equivalent; has a history of
exposure to humans and the
environment demonstrating minimal
toxicity; and has a non-toxic mode of
action to the target pest(s). However, the
Agency has occasionally required such
data for microbial pesticides (e.g.,
Metarhizium anisopliae). The microbial
pesticides typically have a limited host
range and affect only certain species
limiting the potential of such pesticides
to pose endangered species concerns.
The Agency anticipates that these data
could be requested in the future in
connection with other registration and
reregistration actions for both
biochemical and microbial pesticides if
lower tier studies show potential
adverse effects to nontarget organisms.
In response to a Data Call-In notice on
certain conventional pesticides for data
on the location of all listed species, an
industry taskforce is working to develop
a database that may partly fulfill Agency
needs, i.e., geographic locations where
potentially affected species are thought
to occur. Access to the task force data
by other registrants who may be
required to provide such data in the
future would be made available through
appropriate data sharing mechanisms.
Although the anticipated expanded
burden on registrants is not large since
it does not entail experimental or
laboratory procedures, it is nevertheless
not likely to be inconsequential. Thus,
the Agency is requesting comment on its
utility and appropriateness.
While EPA is using the best available
scientific and commercial information
to assess risks to listed species,
uncertainties still exist. Further research
and investigation might help to develop
improved risk assessment approaches.
The Agency recognizes that such
research also could lead, in the long
run, to additional data requirements for
registration. Accordingly, the Agency
seeks input on research areas that may
be necessary to effectively characterize
potential risks to listed endangered
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species from pesticide use. These
include research to address the
following types of uncertainties:
• Product use information by
geographic location below the state and
county levels.
• Toxicity data and environmental
fate measurements/exposure model
predictions with end use products.
• Toxicity data from surrogate species
that quantify dose-response
relationships for effects relevant to
critical life stages of endangered species.
• Measured or estimated values of
physiological, biochemical, and
morphological characteristics of
endangered species and surrogate
species to refine chemical-specific
interspecies toxicity extrapolations.
• Toxicity, exposure, uptake, and
elimination data to better determine any
differences in interspecies sensitivity of
nontarget and endangered plant species
exposed to herbicides.
• Toxicity data to characterize
potential effects to aquatic invertebrates
(i.e., freshwater mussels).
• Toxicity data to characterize
potential effects to reptiles and
amphibians.
The Agency seeks comment on:
1. The relative value of each of these
research areas in better refining
assessments of potential risks to listed
species.
2. Input on specific research
directions in these areas, including
methodologies, protocols etc., that
would be appropriate and useful in
assessing the potential risks to listed
species.
3. Other types of research that would
be of value in refining potential risks of
a pesticide to a listed species.
4. The extent to which potential
research areas reflect uncertainties that
apply to pesticides generically; to
chemical stressors generically, or to
types of pesticides or chemicals
stressors.
XII. Research Involving Human
Subjects
This proposed rule (see proposed
§ 158.950) would establish data
requirements for applicator/user
exposure studies for biochemical
pesticides proposed as insect repellents.
This data requirement is consistent with
§ 158.500 of the proposed rule for
conventional pesticides (70 FR 12275,
March 11, 2005).
On January 26, 2006, the EPA
Administrator signed a final rule
entitled Protections for Humans
Subjects in Research (71 FR 6138,
February 6, 2006), (Ref. 23) that
significantly strengthens and expands
the protections for subjects of ‘‘third-
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party’’ human research (i.e., research
that is not conducted or supported by
EPA) by (1) prohibiting new research
involving intentional exposure of
pregnant women or children that is
intended for submission to EPA under
the pesticide laws; (2) extending the
provisions of the Federal Policy for the
Protection of Human Subjects of
Research (the ‘‘Common Rule’’) to other
human research involving intentional
exposure of non-pregnant adults that is
intended for submission to EPA under
the pesticide laws; (3) requiring
submission to EPA of protocols and
related information about covered
human research before it is initiated;
and (4) establishing an independent
Human Studies Review Board to review
both proposals for new research and
reports of covered human research on
which EPA proposes to rely under the
pesticide laws.
This rule forbids EPA to rely, in its
actions under the pesticide laws, on
intentional-exposure human research
that either involves pregnant women or
children as subjects or is otherwise
considered unethical, except in
narrowly defined circumstances. Some
studies required under this part will
also be subject to subparts K, L, and M
of 40 CFR part 26—the newly
promulgated final rule for the protection
of human subjects of research. Subpart
K extends the substantive provisions of
the ‘‘Common Rule’’—the ethical
standard that governs research with
human subjects conducted or supported
by EPA and other Federal departments
and agencies to third-party research that
involves intentional exposure of nonpregnant adults as subjects, and that is
intended for submission to EPA under
the pesticide laws. Subpart K also
requires submission to EPA of proposals
for any covered research, at least 90
days before it is initiated, for review by
EPA staff and the Human Studies
Review Board. Subpart L categorically
prohibits any third-party research that
involves intentional exposure of
pregnant women, fetuses, or children as
subjects, and that is intended for
submission to EPA. Subpart M specifies
the range of information required to be
submitted along with reports of
completed research with human
subjects to document the ethical
conduct of the research.
XIII. Summary of Proposed Changes
The Agency has prepared a document,
entitled Summary of the Proposed
Changes (Ref. 1), to compare the current
data requirements to support the
registration of biochemicals and
microbials, respectively, with the
revised data requirements presented in
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this proposed rule. The changes
include: revision in test notes, revision
in guideline names, revisions in tiering
the various data requirements, etc.
Along with the proposed changes to the
data required, the Agency also proposes
to revise the definitions of biochemical
pesticides and microbial pesticides and
to add definitions of pheromones,
arthropod pheromones, and straight
chain lepidopteran pheromones.
XIV. Summary of Options
What Options did the Agency
Evaluate?
The Agency evaluated three
regulatory options to revising the
existing data requirements. The three
options are generally characterized by
estimated annual cost or regulatory
burden reduction and frequency of
requiring data. The options as presented
are intended to reflect broad conceptual
approaches, and within each broad
option there are other options for
requiring or reducing data requirements.
In addition, whether considered broadly
or more narrowly, EPA’s approach is
based on the primary need for sufficient
information to make the FIFRA/FFDCA
findings while at the same time being
mindful of opportunities to reduce
burden and testing where data is not
value added. Again, as noted
previously, the point is to emphasize
first the need to meet statutory
mandates.
This section will briefly cover these
three options. The specific cost
differences between these three
regulatory options are discussed in the
executive summary of the Economic
Analysis for this rulemaking (Ref. 6).
Overviews of estimated annual cost or
regulatory burden reduction for the
proposed rulemaking as a whole may be
found in Unit XVI., Regulatory
Assessment.
1. Option 1 (reduced regulatory
burden, potential risk). This low-cost
approach was designed to maximize
burden reduction based upon the
specific nature of biochemical and
microbial pesticides. Based on the nontoxic mode of action and naturallyoccurring characteristics of many of
these compounds, the Agency could
perform a complete risk assessment
based on a minimal amount of nontarget
organisms and environmental fate data.
For biochemical pesticides, the Agency
would not require Tier I nontarget
organisms and Tier II environmental
fate data. For example, under this
approach, the Agency would not receive
any exposure or infectivity/
pathogenicity data for biochemical
pesticides. For microbial pesticides, the
Agency would significantly reduce the
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frequency of time (up to 50 percent) that
proposed Tier I nontarget organisms and
Tier II environmental fate data are
required. The nontarget organism tests
monitor the effects of proposed
pesticides on nontarget birds, wild
mammals, fish, insects and plants. The
environmental fate tests are used to
assess the persistence of biochemicals
and microbial pesticides in the
environment. This option would only
minimally reduce the regulatory burden
as compared to the changes being
proposed today (described in Option 3).
The Agency does not believe the
decrease in burden outweighs the loss
in benefits to public health and the
environment from reduced availability
of data for assessing environmental
hazard and risk through registration
decisions. The cost savings realized in
this option are only marginally lower
than the savings realized in the
proposed option.
2. Option 2 (significant regulatory
burden, adequate risk assessment). This
high-cost approach was evaluated based
on an Agency approach of maximizing
the completeness of the database. Under
this approach, the Agency would
require Tier I human health and
environmental data requirements 100
percent of the time. For example, under
this approach, the Agency would
receive all exposure and infectivity/
pathogenicity data, with
immunotoxicity required as Tier II and
Tier III data. This approach would result
in significantly higher costs to pesticide
registrants and increased burden to the
Agency compared to the proposed
approach. Additionally, unlike Option 1
and the proposed option, EPA believes
that this high-cost approach would
substantially raise the cost of registering
a biochemical or microbial pesticide,
resulting in fewer products being
registered and reducing the potential for
these biopesticides (generally lower
risk) to compete in the marketplace to
provide alternatives to conventional
pesticides (generally higher risk). The
extra cost and time required to register
a biochemical or microbial pesticide
under this option may discourage use of
these safer pesticides, resulting in more,
not less environmental risk.
3. Option 3 (proposed option). The
proposed option provides the Agency
with flexibility and is a middle ground
between Option 1, representing a
minimal cost but potentially significant
loss of environmental hazard
information, and Option 2, representing
the maximum availability of
information, but at significantly higher
cost. The Agency would require, under
certain conditions, human health and
environmental data from all tiering
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levels (I, II, III, IV). The frequency that
data is required would be based on
current scientific knowledge and
conditions specific to the active
ingredient and use patterns. For
example, the Agency proposes to
require immunotoxicity as Tier II and
Tier III data, conditionally require
infectivity/pathogenicity data, and
conditionally require exposure data for
insect repellents. The proposed option
is a codification of current practice, and
is a balance that provides sufficient data
for Agency to complete an
environmental risk assessment while
ensuring the lowest feasible cost and
burden to applicants and the Agency.
The Agency believes the changes
proposed today best serve to protect
human health and the environment and
allow for a complete and accurate
assessment of risks, while benefitting a
large number of parties, including the
regulated industry, pesticide users, the
general public, other Federal, State, and
foreign governments, and others who
are affected by or interested in pesticide
use or regulation. Additionally, the net
benefit of the proposed changes is
expected to include a cost savings for
existing and future biochemical and
microbial pesticide registrants versus
the current codified requirements.
Comparing the proposed option to
Option 1 (low cost option), EPA believes
that the modified and newly-imposed
nontarget organisms and environmental
fate Tier I data requirements contained
in the proposed approach are needed to
ensure informed risk assessment and
risk management decisions on
biochemical and microbial pesticide
registrations.
Comparing the proposed option to
Option 2 (high cost option), EPA
believes that the cost and burden of
requiring the Tier I human health and
environmental data for all biochemical
and microbial registrations would not
warrant the modest benefits of
marginally valuable information. EPA
believes that Option 2 would reduce the
adverse externalities of pesticides and
unknown risks to consumers only
slightly more than the proposed
approach. However, the benefits of this
additional data are speculative. Based
on the specific nature and scientific
knowledge of biochemical and
microbial pesticides, these additional
data (over and above what the proposed
option requires) would most likely
inform registration decisions very little.
XV. References
The Agency has established a docket
for this rulemaking under docket ID
number EPA–HQ–OPP–2004–0415. The
following is a listing of the documents
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that are specifically referenced in this
proposed rule. These documents, and
other supporting materials, are included
in the docket. Please note that the
official docket includes the documents
located in the docket as well as the
documents that are referenced in those
documents. As indicated previously, not
all docket materials are available
electronically, but all publicly available
docket materials are available as
described under ADDRESSES.
1. U.S. EPA, 2005. ‘‘Summary of
Proposed Changes to Biochemical and
Microbial Pesticide Data Requirements.’’
FEAD/OPP/U.S. EPA, Washington, D.C.
2. U.S. EPA, 2003. ‘‘OPPTS Test
Guidelines.’’ OPP/U.S. EPA,
Washington, D.C.
3. National Research Council,
‘‘Pesticides in the Diets of Infants and
Children,’’ National Academy Press,
Washington, D.C., 1993. Excerpt pp.
152–156.
4. FIFRA Scientific Advisory Panel
(SAP). 1994 SAP Final, November 29,
1994 FIFRA Scientific Advisory Panel
Meeting, November 29–30, 1994, held in
Arlington, Virginia.
5. U.S. EPA. 2005. Part II.
Environmental Protection Agency.
Pesticides; Data Requirements for
Conventional Pesticides; Proposed Rule.
(70 FR 12276, March 11, 2005).
6. U.S. EPA, 2005. ‘‘Economic
Analysis of the Proposed Rule Changing
Data Requirements for Biochemical and
Microbial Pesticides.’’ FEAD/OPP/U.S.
EPA, Washington, D.C.
7. FIFRA Scientific Advisory Panel
(SAP). ‘‘A Set of Scientific Issues Being
Considered by the Agency in
Connection with Proposed Revision to
Subdivision M, Immunotoxicity Testing
of Biochemical Pest Control Agents
(BPCA’s).’’ Review from open meeting
on March 24, 1987 in Arlington,
Virginia.
8. U.S. EPA, 1989. ‘‘Subdivision M of
the Pesticide Testing Guidelines,
Microbial and Biochemical Pest Control
Agents.’’ EFED/OPP/U.S. EPA,
Washington, D.C.
9. U.S. EPA, 1982. ‘‘Pesticide
Assessment Guidelines, Subdivision M,
Biorational Pesticides.’’ HED/OPP/U.S.
EPA, Washington, D.C.
10. U.S. EPA, 1986. ‘‘Series 875,
Group A, Applicator/user Exposure
Monitoring Guidelines.’’ Presented to
the FIFRA Scientific Advisory Panel
(SAP), January, 1986. OPP/U.S. EPA,
Washington, D.C.
11. U.S. EPA, 2005. ‘‘Overview of
Proposed Data Requirements and FIFRA
SAP Review.’’ FEAD/OPP/U.S. EPA,
Washington, D.C.
12. U.S. EPA, 2005. ‘‘Analysis of Data
Requirements for Biochemical and
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Microbial Pesticides from 1997–2004.’’
FEAD/OPP/U.S. EPA, Washington, D.C.
13. U.S. EPA, 2005. ‘‘Data
Requirements for Biochemical and
Microbial Pesticides; Proposed Rule;
Consultations.’’ FEAD/OPP/U.S. EPA,
Washington, D.C.
14. U.S. EPA, 2005. ‘‘Comparison
between Current Conventional
Pesticides Data Requirements and
Proposed Biochemical and Microbial
Pesticide Data Requirements.’’ FEAD/
OPP/U.S. EPA, Washington, D.C.
15. OECD [2002-a] Guidance for
Registration Requirements for
Pheromones and Other Semiochemicals
Used for Arthropod Pest Control. OECD
Series on Pesticides, Number 12.
Organization for Economic Cooperation
and Development. February 26, 2002.
16. U.S. EPA, 2000. ‘‘p-Menthane-3,8diol (011550) Biopesticide Registration
Eligibility Document.’’ BPPD/OPP/U.S.
EPA, Washington, D.C. Issued May,
2000.
17. OECD [2002–b] Registration of
Agricultural Pesticides, Biological
Pesticides—Progress on Development of
Dossier/Monograph Guidance for
Microbials and Pheromones. Working
Group on Pesticides. Organization for
Economic Cooperation and
Development. January 3, 2002.
18. U.S. EPA, 2002. ‘‘Supporting
Statement for an Information Collection
Request: Tolerance Petitions for
Pesticides on Food/Feed Crops and New
Inert Ingredients.’’ OMB Control No.
2070–0024, EPA ICR No. 0597. OPP/
U.S. EPA, Washington, D.C.
19. U.S. EPA, 2002. ‘‘Supporting
Statement for an Information Collection
Request: Application for New or
Amended Pesticide Registration.’’ OMB
Control No. 2070–0060, EPA ICR No.
0277. OPP/U.S. EPA, Washington, D.C.
20. U.S. EPA, 2001. ‘‘Supporting
Statement for an Information Collection
Request: ’’Data Generation for
Reregistration; Phase 4 and 5
Reregistration.‘‘ OMB Control No. 2070–
0107, EPA ICR No. 1504. OPP/U.S. EPA,
Washington, D.C.
21. U.S. EPA, 2001. ‘‘Supporting
Statement for an Information Collection
Request: Data Call-Ins for the Special
Review and Registration Review
Programs.’’ OMB Control No. 2070–
0057, EPA ICR No. 0057. OPP/U.S. EPA,
Washington, D.C.
22.U.S. EPA, 2004. ‘‘Supporting
Statement for an Information Collection
Request: Plant- Incorporated
Protectants; CBI Substantiation and
Adverse Effects Reporting.’’ OMB
Control No. 2070–0142, EPA ICR No.
1693, Washington, D.C.
23. U.S. EPA, 2005. Protections for
Subjects in Human Research: Final
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Rule. (71 FR 6138, February 6, 2006).
Document ID No. OPP–2003–0132.
XVI. FIFRA Review Requirements
In accordance with FIFRA section
25(a), the Agency submitted a draft of
this proposed regulation to the FIFRA
SAP, the USDA, the Committee on
Agriculture in the House of
Representatives, and the Committee on
Agriculture, Nutrition, and Forestry in
the United States Senate.
The FIFRA SAP waived its review of
this proposal because the significant
scientific issues involved have already
been reviewed by the SAP and
additional review isn’t necessary. USDA
participated fully in the interagency
review process under Executive Order
12866, during which EPA and USDA
discussed the registration process of
microbial pesticides and the need for a
coordination process when an APHIS
movement permit under 7 CFR part 340
is required by USDA. As a part of
related comments, USDA suggested that
the Agency consider requiring the
registrants to submit a copy of the
applicable APHIS permits as part of the
registration application for a microbial
pesticide because it would facilitate
coordination and improve compliance
with the applicable USDA requirements.
As discussed in Unit IIX., the Agency is
specifically seeking public comment on
the most appropriate method to ensure
APHIS permitting and EPA registrations
are properly coordinated.
XVII. Regulatory Assessment
A. Regulatory Planning and Review
Under Executive Order 12866,
entitled Regulatory Planning and
Review (58 FR 51735, October 4, 1993),
the Office of Management and Budget
(OMB) has determined that this
proposed rule is a ‘‘significant
regulatory action’’ because the proposed
revision of the existing regulation to
update the data requirements may raise
novel legal or policy issues arising out
of legal mandates, the President’s
priorities, or the principles set forth in
the Executive Order. Accordingly, EPA
submitted this proposed rulemaking to
OMB for review under Executive Order
12866 and any changes made in
response to OMB comments have been
documented in the docket for this
rulemaking as required by sec. 6(a)(3)(E)
of the Executive Order.
In addition, EPA has prepared an
economic analysis of the potential costs,
benefits, and impacts associated with
this proposed action, which is
contained in a document entitled
Economic Analysis of the Proposed Rule
Changing Data Requirements for
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Biochemical and Microbial Pesticides
(Ref. 6). A copy of this Economic
Analysis is available in the docket for
this action, and is briefly summarized
here.
The economic analysis considered the
incremental effects between the baseline
and future biochemical and microbial
pesticide registration activity based on
the proposed rule and two alternatives.
All costs associated with presently
codified 40 CFR part 158 data
requirements applicable to biochemical
and microbial pesticides were
considered in the baseline. Future
biochemical and microbial registration
activity and associated costs were
calculated based on a historical
examination of actual pesticide
registration actions between 1997 and
2004 combined with anticipated effects
of new, revised, or modified 40 CFR part
158 subparts L and M data
requirements. Review of 1997 to 2004
registration activity considered the type
and frequency of the various
biochemical and microbial pesticide
registration actions that occurred, the
related applicability of the various data
requirements for those actions, the type
and regularity of waivers granted by
EPA for certain data requirements, and
information about the applicants
involved in those actions. Where
applicable, these trends and patterns
were used to predict future registration
activity. Additional effects of the
proposed rule due to newly proposed,
revised, or modified 40 CFR part 158
subparts L and M data requirements
were estimated based on EPA
experience and best judgment.
Most of the data requirements
contained in this proposal have been
applied on a case-by-case basis over the
years to reflect the evolution of
scientific understanding and concerns.
The proposed revisions include newly
codified data requirements (i.e., data
requirements that are not currently in
part 158, but have been, in practice,
required on a case-by-case basis),
changes to existing requirements (i.e., a
change in frequency with which a
currently codified data requirement
would be imposed. For example, a
change from conditionally-required to
required, or visa versa, or a change in
use pattern for an existing requirement),
and newly imposed data requirements
(i.e., data requirement have never been
previously imposed).
To calculate the potential costs
associated with this proposal, EPA first
identified the tests necessary to generate
the data required, and then gathered
information on the prices that
laboratories typically charge a firm to
conduct these tests. The prices varied
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depending on conditions specific to the
substance tested. Variations can be
related to differences in the assumptions
about the test performed (e.g., protocol,
species used), or can simply be a
difference in the price charged by the
laboratory. Average, high, and low cost
estimates were obtained for each test
where possible. EPA assumed that the
data required would always need to be
newly generated, but often the data are
already available because the registrant
generated it for its own use. In such
cases, the firm would simply need to
submit those data to EPA, which
involves less burden than generating it.
EPA then used historical data on
pesticide registration actions that
occurred over an eight year period
(1997–2004) to identify the entities that
sought pesticide registration actions in
the past (Ref. 12). The data required for
each registration action depends on
several factors, including the type of
registration action (e.g., registration of a
new active ingredient food use,
registration of a new active ingredient
non-food use, registration and
amendments to registrations involving a
major new use) and use pattern (how
the product will be used). To estimate
the average incremental cost of a new
registration, a baseline testing rate (i.e.,
the percentage of time a particular test
was historically required under the
current rule) was estimated by EPA
scientists based on their past experience
with biochemical and microbial
pesticide registrations and their
involvement in developing the new data
requirements. This baseline data
requirement rate was compared with the
percentage of time each test was
required for registrations between 1997
and 2004. EPA assumes that under the
proposed rule, data requirements would
be imposed at the same frequency they
have been required from 1997 to 2004.
Additionally, EPA scientists estimated
the frequency that newly imposed data
requirements would be required.
Part of the Economic Analysis
included preparation of an industry
profile using the same historical data on
pesticide registration actions to identify
the companies involved in those
actions, and based it on public
information gathered about those
companies. EPA also used this industry
profile to analyze the potential impacts
of the proposed rule on small
businesses, the results of which are
summarized in Unit XVII.C. The
incremental costs and a more detailed
discussion of the estimating
methodology employed in the analysis
are presented in the economic impact
analysis prepared for this proposed rule
(Ref. 6).
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Using the currently codified
requirements as the baseline for the
impact analysis, the total annual impact
to the pesticide industry is estimated to
be a regulatory compliance cost
reduction of about $3.04 million per
year, with an estimated average cost
reduction of $60,000 per firm per year.
EPA also considered a low cost
alternative and a high cost alternative to
the proposed rule. The low cost
alternative would waive certain data
requirements for biochemical pesticides
and reduce the rate at which certain
data requirements are required for
microbial pesticides. The estimated
impact of the low cost alternative is
estimated to be a regulatory compliance
cost reduction approximately $3.20
million, with an estimated average cost
reduction of $63,000 per firm per year.
The high cost alternative would require
certain groups of data requirements 100
percent of the time, removing the
discretion of Agency scientists to decide
if the data are needed for a specific
registration. This alternative would
result in an estimated annual cost
increase over current rule requirements
of approximately $3.44 million per year,
or an estimated cost increase of $67,000
per firm.
The estimated potential costs of the
proposed rule acknowledges registrant
is likely to request that the Agency
waive certain data requirements if the
registrant believes that the data are not
necessary for determining the effects of
a pesticide on human health and the
environment. EPA estimated the annual
cost savings due to waived data
requirements based on both the
historical rate and type of waivers
granted for the period from 1997–2004,
and on an analysis of how the proposed
rule is expected to modify the rate at
which waivers are granted. EPA
estimated that the annual cost savings
due to waived data requirements based
on the historic waiver rates to be
approximately $29.6 million, or
$580,000 per firm per year. At the
modified waiver rates predicted under
the proposed rule, EPA estimated an
annual cost savings of $23.96 million, or
$470,000 per firm per year.
Since the likely impact of the
proposed rule on businesses overall is
expected to be mostly beneficial, the
Agency believes that the rule would
have no effect on the availability of
pesticides to users. On balance, the
Agency believes that cost savings
resulting from the proposed changes to
40 CFR part 158 subparts L and M can
be realized without compromising the
protection of human health and the
environment.
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B. Paperwork Reduction Act
This proposed rule does not contain
any information collection requirements
that require additional approval by the
Office of Management and Budget
(OMB) under the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq. Pursuant to
the Paperwork Reduction Act (PRA), 44
U.S.C. 3501 et seq., an agency may not
conduct or sponsor, and a person is not
required to respond to an information
collection request unless it displays a
currently valid OMB control number.
The OMB control numbers for EPA’s
regulations contained in Title 40 of the
CFR, after appearing in the preamble of
the final rule, may be listed in 40 CFR
part 9, and included on the related
collection instrument (e.g., form or
survey).
Under 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 needed to:
review instructions; develop, acquire,
install, and utilize technology and
systems for the purposes of collecting,
validating, and verifying information,
processing and maintaining
information, and disclosing and
providing information; adjust the
existing ways to comply with any
previously applicable instructions and
requirements; train personnel to be able
to respond to a collection of
information; search data sources;
complete and review the collection of
information; and transmit or otherwise
disclose the information.
EPA has determined that this
proposed rule imposes no additional
information collection and paperwork
burden. The information collection
requirements, i.e., the paperwork
collection activities, contained in this
proposal related to the new data
necessary to register a pesticide product
are already approved by OMB under
several existing information collection
requests (ICR). Specifically, the program
activities which would generate a
paperwork burden under this proposal
are covered by the following ICRs:
The activities associated with the
establishment of a tolerance are
currently approved under OMB Control
No. 2070–0024 (EPA ICR No. 0597) (Ref.
18);
The activities associated with the
application for a new or amended
registration of a pesticide are currently
approved under OMB Control No. 2070–
0060 (EPA ICR No. 0277) (Ref. 19);
The activities associated with the
generation of data for reregistration are
currently approved under OMB Control
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No. 2070–0107 (EPA ICR No. 1504) (Ref.
20);
The activities associated with the
generation of data for special review or
registration review are currently
approved under OMB Control No. 2070–
0057 (EPA ICR No. 0922) (Ref. 21); and
Notification of genetically modified
microbial pesticides. OMB Control No.
2070–0142 (EPA ICR No. 1693) (Ref. 22).
These existing ICRs cover the
paperwork activities contained in this
proposal because these activities already
occur as part of existing program
activities. These program activities are
an integral part of the Agency pesticide
program and the corresponding ICRs are
regularly renewed as required under the
PRA, such that these OMB Control Nos.
are maintained valid. The approved
burden in these ICRs were increased in
1996 to accommodate the potential
increased burden related to the
implementation of the new safety
standard imposed in 1996 by FQPA and
additional burden revisions related to
the proposed rule are not necessary.
Based on these existing approvals, the
Agency estimates that the total average
annual public reporting burden
currently approved by OMB for these
various activities ranges from 8 hours to
approximately 3,000 hours per
respondent, depending on the activity
and other factors surrounding the
particular pesticide product. Additional
information about this estimate is
provided in the Economic Analysis for
this rulemaking.
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
docket that has been established for this
proposed rule (docket ID number EPA–
HQ–OPP–2004–0415) at https://
www.epa.gov/edocket/.
The Agency will consider and address
comments received on the information
collection requirements contained in
this proposal when it develops the final
rule.
C. Regulatory Flexibility Act
Pursuant to section 605(b) of the
Regulatory Flexibility Act (RFA), 5
U.S.C. 601 et seq., after considering the
potential economic impacts of today’s
proposed rule on small entities, the
Agency hereby certifies that this
proposal will not have a significant
adverse economic impact on a
substantial number of small entities.
This determination is based on the
Agency’s economic analysis performed
for this rulemaking, which is
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summarized in Unit XVII.A., and a copy
of which is available in the docket for
this rulemaking. The following is a brief
summary of the factual basis for this
certification.
Small entities include small
businesses, small organizations, and
small governmental jurisdictions. For
purposes of assessing the impacts of
today’s proposed rule on small entities,
small entity is defined in accordance
with the RFA as: (1) A small business
as defined by the Small Business
Administration’s (SBA) regulations at 13
CFR 121.201; (2) a small governmental
jurisdiction that is a government of a
city, county, town, school district, or
special district with a population of less
than 50,000; and (3) a small
organization that is any not-for-profit
enterprise which is independently
owned and operated and is not
dominant in its field.
Based on the industry profile that
EPA prepared using historical data as
part of the Economic Analysis prepared
for this rulemaking, EPA has
determined that this proposed rule is
not expected to impact any small notfor-profit organizations or small
governmental jurisdictions. As such, the
small entity impacts analysis prepared
as part of the economic analysis
evaluated potentially impacted
businesses that could be considered
small businesses as defined by the
Small Business Administration, which
uses the maximum number of
employees or sales for businesses in
each industry sector, as that sector is
defined by NAICS. For example, entities
defined as Pesticide and Other
Agricultural Chemical Manufacturing
(325320) are considered to be a small
business if they employ 500 or fewer
people.
EPA then used historical data to
estimate the impacts of the proposed
rule on these small businesses. Out of
51 firms with biochemical or microbial
registration actions between 1997 to
2004, financial data for determining
company size was available for 40 firms,
with 23 of those firms classified as small
businesses. According to the analysis,
all of these small entities would have
realized a reduction in costs based on
the proposed rule changes compared to
the current part 158 data requirements.
Given these estimated impacts on small
businesses, EPA concluded that the
proposed revisions may benefit and
would not likely have a significant
adverse economic impact on a
substantial number of small entities.
Nonetheless, EPA is particularly
interested in receiving comment from
small businesses as to the estimated cost
savings, expected benefits, and overall
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impacts of this proposed rule. Any
comments regarding the economic
impacts that this proposed regulatory
action may impose on small entities
should be submitted to the Agency in
the manner specified in the ADDRESSES
section.
D. Unfunded Mandates Reform Act
Under Title II of the Unfunded
Mandates Reform Act of 1995 (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 for State, local, and tribal
governments, in the aggregate, or the
private sector in any one year. As
described in Unit XVII, the total annual
impact to the pesticide industry is
estimated to be a regulatory compliance
cost reduction of about $3.04 million
per year. In addition, since State, local,
and tribal governments are rarely a
pesticide applicant or registrant, the
proposed rule is not expected to
significantly or uniquely affect small
governments.
Accordingly, this action is not subject
to the requirements of sections 202 and
205 of UMRA.
E. Federalism Implications
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
would 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 the Order. Because
instances where a State is a registrant
are extremely rare, this proposed rule
may seldom affect a State government.
Thus, Executive Order 13132 does not
apply to this proposed rule. In the spirit
of the Order, and consistent with EPA
policy to promote communications
between the Agency and State and local
governments, EPA specifically solicits
comment on this proposed rule from
State and local officials.
F. Tribal Implications
As required by Executive Order
13175, entitled Consultation and
Coordination with Indian Tribal
Governments (65 FR 67249, November
6, 2000), EPA has determined that this
proposed rule does not have tribal
implications because it would not have
substantial direct effects on tribal
governments, on the relationship
between the Federal government and
the Indian tribes, or on the distribution
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of power and responsibilities between
the Federal government and Indian
tribes, as specified in the Order. At
present, no tribal governments hold, or
have applied for, a pesticide
registration. Thus, Executive Order
13175 does not apply to this proposed
rule. In the spirit of the Order, and
consistent with EPA policy to promote
communications between the Agency
and tribal governments, EPA
specifically solicits comment on this
proposed rule from tribal officials.
G. Protection of Children
Executive Order 13045, entitled
Protection of Children from
Environmental Health Risks and Safety
Risks (62 FR 19885, April 23, 1997) does
not apply to this proposed rule because
this action is not designated as an
‘‘economically significant’’ regulatory
action as defined by Executive Order
12866 (see Unit XVII.A.). Further, this
proposal does not establish an
environmental standard that is intended
to have a negatively disproportionate
effect on children. To the contrary, this
action would provide added protection
for children from pesticide risk. The
proposed data requirements are
intended to address risks that, if not
addressed, could have a
disproportionate negative impact on
children. EPA would use the data and
information obtained by this proposed
rule to carry out its mandate under
FFDCA to give special attention to the
risks of pesticides to sensitive
subpopulations, especially infants and
children.
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H. Energy Implications
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 likely to have
any significant adverse effect on the
supply, distribution, or use of energy.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (NTTAA), 15 U.S.C. 272
note) directs EPA to use voluntary
consensus standards in its regulatory
activities unless to do so would be
inconsistent with applicable law or
impractical. Voluntary consensus
standards are technical standards (e.g.,
materials specifications, test methods,
sampling procedures, etc.) that are
developed or adopted by voluntary
consensus standards bodies. NTTAA
directs EPA to provide Congress,
through OMB, explanations when the
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Agency decides not to use available and
applicable voluntary consensus
standards. This regulation proposes the
types of data to be required to support
conventional pesticide registration but
does not propose to require specific
methods or standards to generate those
data. Therefore, this proposed
regulation does not impose any
technical standards that would require
Agency consideration of voluntary
consensus standards. The Agency
invites comment on its conclusion
regarding the applicability of voluntary
consensus standards to this rulemaking.
J. Environmental Justice
This proposed rule does not have an
adverse impact on the environmental
and health conditions in low-income
and minority communities. Therefore,
under Executive Order 12898, entitled
Federal Actions to Address
Environmental Justice in Minority
Populations and Low-Income
Populations (59 FR 7629, February 16,
1994), the Agency has not considered
environmental justice-related issues.
List of Subjects
40 CFR Part 158
Administrative practice and
procedure, Agricultural commodities,
Pesticides and pests, Reporting and
recordkeeping requirements.
40 CFR Part 172
Confidential business information,
Pesticides and pests, Reporting and
recordkeeping requirements,
Administrative practice and procedure,
Agricultural commodities,
Intergovernmental relations, Labeling.
Dated: March 1, 2006.
Stephen L. Johnson,
Administrator.
Therefore, it is proposed that 40 CFR
chapter I, parts 158 and 172 be amended
as follows:
PART 158—[AMENDED]
1. By revising the authority citation
for part 158 to read as follows:
Authority: 7 U.S.C. 136–136y; 21 U.S.C.
346a.
2. By adding § 158.3 to part 158,
subpart A to read as follows:
§ 158.3
Definitions.
All terms defined in sec. 2 of the
Federal Insecticide, Fungicide, and
Rodenticide Act apply to this part and
are used with the meaning given in the
Act. Applicable terms from the Federal
Food, Drug, and Cosmetic Act also
apply to this part. Individual subparts
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may contain definitions that pertain
solely to that subpart. The following
additional terms apply to this part:
Active ingredient means any
substance (or group of structurally
similar substances, if specified by the
Agency) that would prevent, destroy,
repel or mitigate any pest, or that
functions as a plant regulator, desiccant,
defoliant, or nitrogen stabilizer, within
the meaning of FIFRA section 2(b).
End-use product means a pesticide
product whose labeling:
(1) Includes directions for use of the
product (as distributed or sold, or after
combination by the user with other
substances) for controlling pests or
defoliating, desiccating or regulating
growth of plants, or as a nitrogen
stabilizer, and
(2) Does not state that the product
may be used to manufacture or
formulate other pesticide products.
Formulation means: (1) The process of
mixing, blending, or dilution of one or
more active ingredients with one or
more other active or inert ingredients,
without an intended chemical reaction,
to obtain a manufacturing-use product
or an end-use product, or
(2) The repackaging of any registered
product.
Impurity means any substance (or
group of structurally similar substances
if specified by the Agency), in a
pesticide product other than an active
ingredient or an inert ingredient,
including unreacted starting materials,
side reaction products, contaminants,
and degradation products.
Impurity associated with an active
ingredient means:
(1) Any impurity present in the
technical grade of active ingredient; and
(2) Any impurity which forms in the
pesticide product through reactions
between the active ingredient and any
other component of the product or
packaging of the product.
Inert ingredient means any substance
(or group of structurally similar
substances if designated by the Agency),
other than the active ingredient, which
is intentionally included in a pesticide
product.
Integrated system means a process for
producing a pesticide product that:
(1) Contains any active ingredient
derived from a source that is not an
EPA-registered product; or
(2) Contains any active ingredient that
was produced or acquired in a manner
that does not permit its inspection by
the Agency under FIFRA sec. 9(a) prior
to its use in the process.
Manufacturing-use product means
any pesticide product other than an
end-use product. A product may consist
of the technical grade of active
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(1) Is a naturally-occurring substance
or structurally-similar and functionally
identical to a naturally-occurring
substance;
ingredient only, or may contain inert
ingredients, such as stabilizers or
solvents.
Starting material means a substance
used to synthesize or purify a technical
grade of active ingredient (or the
practical equivalent of the technical
grade ingredient if the technical grade
cannot be isolated) by chemical
reaction.
Technical grade of active ingredient
means a material containing an active
ingredient:
(1) Which contains no inert
ingredient, other than one used for
purification of the active ingredient; and
(2) Which is produced on a
commercial or pilot plant production
scale (whether or not it is ever held for
sale).
§ 158.65
[Removed]
3. By removing § 158.65.
4. By adding subparts L and M to part
158 to read as follows:
Subpart L—Biochemical Pesticides
Sec.
158.900 Biochemical pesticides subject to
subpart L.
158.910 Biochemical pesticides data
requirements.
158.930 Product chemistry data
requirements table.
158.940 Residue data requirements table.
158.950 Human health assessment data
requirements table.
158.960 Nontarget organisms and
environmental fate data requirements
table.
158.970 Biochemical pesticides product
performance data requirements.
Subpart M— Microbial Pesticides
Sec.
158.1000 Definition and applicability.
158.1010 Microbial pesticide data
requirements.
158.1020 Product analysis data
requirements table.
158.1030 Residue data requirements table.
158.1040 Toxicology data requirements
table.
158.1050 Nontarget organisms and
environmental fate data requirements
table.
158.1060 Microbial pesticides product
performance data requirements.
Subpart L—Biochemical Pesticides
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§ 158.900 Biochemicalpesticides subject
to subpart L.
(a) This subpart applies to all
biochemical pesticides as defined in
paragraphs (b), (c) and (d) of this
section.
(b) Definition. A biochemical
pesticide is a pesticide that:
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(2) Has a history of exposure to
humans and the environment
demonstrating minimal toxicity, or in
the case of a synthetically-derived
biochemical pesticides, is equivalent to
a naturally-occurring substance that has
such a history; and
(3) Has a non-toxic mode of action to
the target pest(s).
(c) Pheromone is a compound
produced by a living organism which,
alone or in combination with other such
compounds, modifies the behavior of
other individuals of the same species.
(1) Arthropod pheromone is a
pheromone produced by a member of
the taxonomic phylum Arthropoda.
(2) Lepidopteran pheromone is an
arthropod pheromone produced by a
member of the insect order Lepidoptera.
(3) Straight Chain Lepidopteran
pheromone is a lepidopteran
pheromone designated by an
unbranched aliphatic chain (between 9
and 18 carbons) ending in an alcohol,
aldehyde, or acetate functional group
and containing up to three bonds in the
aliphatic backbone.
(d) Examples. Biochemical pesticides
include, but are not limited to:
(1) Semiochemicals (insect
pheromones and kairomones),
(2) Natural plant and insect
regulators,
(3) Naturally-occurring repellents and
attractants, and
(4) Enzymes
(e) Applicability. The Agency may
review on a case-by-case basis,
naturally-occurring pesticides that do
not clearly meet the definition of a
biochemical in an effort, to ensure, to
the greatest extent possible, that only
the minimum testing sufficient to make
scientifically sound regulatory decisions
would be conducted. The Agency will
reviewapplications for registration of
naturally-occurring pesticides to
determine whether to review the
pesticide under this subpart L.
§ 158.910 Biochemicalpesticides data
requirements.
(a) Sections 158.930 through 158.970
identify the data requirements that are
required to support registration of
biochemical pesticides. Variations in
the test conditions are identified within
the test notes. Definitions that apply to
all biochemical data requirements can
be found in§ 158.930.
(b) Each data table includes ‘‘use
patterns’’ under which the individual
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12101
data are required, with variations
including food and nonfood uses for
terrestrial and aquatic applications,
greenhouse, indoor, forestry, and
residential outdoor applications under
certain circumstances.
(c) The categories for each data
requirement are ‘‘R’’, which stands for
required, and ‘‘CR’’ which stands for
conditionally required. If a bracket
appears around the R or CR, the data are
required for both the registration and
experimental use permit requests.
Generally, ‘‘R’’ indicates that the data
are more likely required than forthose
data requirements with CR. However, in
each case, the regulatory text preceding
the data table and the test notes
following the data table must be used to
determine whether the data requirement
must be satisfied.
(d) Each table identifies the test
substance that is required to be tested to
satisfy the data requirement. Test
substances may include: technical grade
active ingredient (TGAI),
manufacturing-use product (MP), enduse product (EP), typical end-use
product (TEP), residue of concern, and
pure active ingredient (PAI) or (All)
indicating all of the above.
Commasbetween the test substances
(i.e., TGAI, EP) indicate that data may
be required on the TGAI or EP or both
depending on the conditions set forth in
the test note. Data requirements which
list two test substances (i.e., TGAI and
EP) indicate that both are required to be
tested. Data requirements that list only
the manufacturing product (MP) as the
test substance apply toproducts
containing solely the technical grade of
the active ingredient and
manufacturing-use products to which
other ingredients have been
intentionally added. Data requirements
listing the EP as the test substance apply
to any EP with an ingredient in the enduse formulation other than the active
ingredient that is expected to enhance
the toxicity of the product.
(e) The data requirements are
organized into a tier-testing system with
specified additional studies at higher
tiers being required if warranted by
adverse effects observed in lower tier
studies. The lower tier studies are a
subset of those required for
conventional pesticides, and the studies
overall are generally selected from those
required for conventional pesticides.
(f) Two sets of guideline numbers are
provided for some of the environmental
fate data requirements. For ease of
understanding, the current guidelines
will be used as an interim measure until
the new guidelines (in parentheses) are
finalized.
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§ 158.930 Product chemistrydata
requirements table.
(a) General. (1) Sections 158.100
through 158.130 describe how to use
this table to determine the product
chemistry data requirements for a
particular pesticide product. Notes that
apply to an individual test and include
specific conditions, qualifications, or
exceptions to the designated test are
listed in paragraph (e) of the section.
(2) Depending on the results of the
required product chemistry studies,
appropriate use restrictions, labeling
requirements, or special packaging
requirements may be imposed.
(3) All product chemistry data, as
described in this section, are required to
be submitted to support a request for an
experimental use permit.
(b) Use patterns. Product chemistry
data are required for all pesticide
products and are not use specific.
(c) Key. R=Required; [R]=Required for
registrations andexperimental use
permits; CR=Conditionally required;
[CR]=Conditionally required for
registrations and experimental use
permits; NR=Not required;
MP=Manufacturing-use product;
EP=End-use product; TEP=Typical enduse product; TGAI=Technical grade of
the active ingredient; Residue of
concern= the active ingredient and its
metabolites, degradates, and impurities
of toxicological concern; All= all of the
above. Specific conditions,
qualifications, or exceptions to the
designated test procedures appear in
paragraph (e) of this section, and apply
to the individual tests in the following
table:
(d) Table. The following table shows
the data requirements for biochemical
product chemistry. The test notes are
shown in paragraph (e) of this section.
TABLE—BIOCHEMICAL PRODUCT CHEMISTRY DATA REQUIREMENTS
Guideline Number
Test Substance
to support
All Use
Patterns
Data Requirement
MP
Test notes
EP
Product Identity and Composition
880.1100
Product identity and composition
[R]
TGAI, MP
TGAI, EP
1,2
880.1200
Description of starting materials, production and formulation process
[R]
TGAI, MP
TGAI, EP
2,3
880.1400
Discussion of formation of impurities
[R]
TGAI and
MP
TGAI and
MP
4
830.1700
Preliminary analysis
[CR]
TGAI and
MP
TGAI and
MP
5,8
830.1750
Certified limits
[R]
MP
EP
6
830.1800
Enforcement analytical method
[R]
MP
EP
7
830.6302
Color
[R]
TGAI
TGAI
8
830.6303
Physical state
[R]
TGAI
TGAI and
EP
8
830.6304
Odor
[R]
TGAI
TGAI
8
830.6313
Stability to normal and elevated temperatures, metals and metal ions
[R]
TGAI
TGAI
8,17
830.6315
Flammability
[CR]
MP
EP
9
830.6317
Storage stability
[R]
MP
EP
—
830.6319
Miscibility
[CR]
MP
EP
10
830.6320
Corrosion characteristics
[R]
MP
EP
—
830.7000
pH
[CR]
TGAI and
MP
TGAI and
EP
8,11
830.7050
UV/Visible light absorption
[R]
TGAI
TGAI
—
830.7100
Viscosity
[CR]
MP
EP
12
830.7200
Melting point/melting range
[CR]
TGAI
TGAI
8,13
830.7220
Boiling point/boiling range
[CR]
TGAI
TGAI
8,14
Analysis and Certified Limits
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Physical and Chemical Characteristics
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12103
TABLE—BIOCHEMICAL PRODUCT CHEMISTRY DATA REQUIREMENTS—Continued
Guideline Number
Test Substance
to support
All Use
Patterns
Data Requirement
MP
Test notes
EP
830.7300
Density/relative density/bulk density
[R]
TGAI and
MP
TGAI and
EP
8,18
830.7520
Particle size, fiber length, and diameter
distribution
[CR]
TGAI
TGAI
8,15
830.7550
830.7560
830.7570
Partition coefficient (n-Octanol /Water)
[CR]
TGAI
TGAI
16
830.7840
Water solubility
[R]
TGAI
TGAI
8
830.7950
Vapor pressure
[R]
TGAI
TGAI
8,19
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(e) Test notes. The following test
notes are applicable to the data
requirements for biochemical product
chemistry and are referenced in the last
column of the table in paragraph (d) of
this section.
1. Data must be provided in accordance
with § 158.320.
2. If the MP and EP are produced by an
integrated formulation system(non-registered
source), these data are also required on TGAI.
3. Data must be provided in accordance
with § 158.325,§ 158.330, and § 158.335.
4. Data must be provided in accordance
with § 158.340.
5. Data must be provided in accordance
with § 158.345. Also, required to support the
registration of each manufacturing-use
product (including registered TGAIs) and
end-use products produced by an integrated
formulation system. Data on other end-use
products would be required on a case-by-case
basis. For pesticides in the production stage,
a preliminary product analytical method and
data would suffice to support an
experimental use permit.
6. Data must be provided in accordance
with § 158.350.
7. Data must be provided in accordance
with § 158.355.
8. If the TGAI cannot be isolated, data are
required on the practical equivalent of the
TGAI. EP testing may also be appropriate.
9. Required if the product contains
combustible liquids.
10. Required if the product is an
emulsifiable liquid and is to be diluted with
petroleum solvents.
11. Required if the test substance is soluble
or dispersible in water.
12. Required if the product is a liquid.
13. Required when the technical chemical
is a solid at room temperature.
14. Required when the technical chemical
is a liquid at room temperature.
15. Required for water insoluble test
substances (<10-6 g/l) andfibrous test
substances with diameter ≥0.1 µm.
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16. Required for organic chemicals unless
they dissociate in water or are partially or
completely soluble in water.
17. Data on the stability to metals and
metal ions is required only if the active
ingredient is expected to come in contact
with either material during storage.
18. True density or specific density are
required for all test substances. Data on bulk
density is required for MPs or EPs that are
solid at room temperature.
19. Not required for salts.
§ 158.940
Residue datarequirements table.
(a) General. Sections 158.100 through
§ 158.130 describe how to use this table
to determine the biochemical pesticides
residue data requirements for a
particular pesticide product and the
substance that needs to be tested. These
data requirements apply to all
biochemicals, e.g., semiochemicals,
natural plant and insect regulators,
naturally-occurring repellents and
attractants, and enzymes. Notes that
apply to an individual test and include
specific conditions, qualifications, or
exceptions to the designated test are
listed in paragraph (e) of this section.
(b) Use patterns. (1) Data are required
or conditionally required for all
pesticides used in or on food and for
residential outdoor uses where food
crops are grown. Food use patterns
include products classified under the
general use patterns of terrestrial food
crop use, terrestrial feed crop use,
aquatic food crop use, greenhouse food
crop use, and indoor food use. Data are
also conditionally required for aquatic
nonfood use if there is direct
application to water.
(2) Data may be required for nonfood
uses if pesticide residues may occur in
food or feed as a result of the use. Data
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requirements for these nonfood uses
would be determined on a case-by-case
basis. For example, most products used
in or near kitchens require residue data
for risk assessment purposes even
though tolerances may not be necessary
in all cases. Food uses in general require
a more extensive database to
characterize the extent of the exposure,
whereas nonfood uses which are of
shorter duration, may require fewer
studies. Uses include products
classified under the general use patterns
of terrestrial and aquatic food use,
greenhouse food use, indoor food use,
and indoor residential use.
(c) Key. R=Required; [R]=Required for
registrations andexperimental use
permits; CR=Conditionally required;
[CR]=Conditionally required for
registrations and experimental use
permits; NR=Not required;
MP=Manufacturing-use product;
EP=End-use product; TEP=Typical enduse product; TGAI=Technical grade of
the active ingredient; Residue of
concern= the active ingredient and its
metabolites, degradates, and impurities
of toxicological concern; All= all of the
above. Specific conditions,
qualifications, or exceptions to the
designated test procedures appear in
paragraph (e) of this section, and apply
to the individual tests in the following
table:
(d) Table. The following table shows
the data requirements for biochemical
residue for specific uses. The test notes
are shown in paragraph (e) of this
section.
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TABLE—BIOCHEMICAL RESIDUE DATA REQUIREMENTS FOR SPECIFIC USES
Use patterns containing data requirements
Guideline Number
Data Requirement
Terrestrial
Aquatic
Food/Feed
Food
Greenhouse
Food
Test Substance
Test notes
Indoor Food
Supporting Information
860.1100
Chemical identity
[CR]
[CR]
[CR]
[CR]
TGAI
1,2,4
860.1200
Directions for use
[CR]
[CR]
[CR]
[CR]
TGAI
1,3,4
860.1300
Nature of the residue in
plants
[CR]
[CR]
[CR]
[CR]
TGAI
1,4,5,6
860.1300
Nature of the residue in
livestock
[CR]
[CR]
[CR]
[CR]
TGAI
1,7,8,10
860.1340
Residue analytical methodplants
Residue analytical methodlivestock
CR
CR
R
[CR]
Residue of concern
4,9,10
860.1360
Multiresidue method
CR
CR
R
CR
Residue of concern
10,11
Nature of Residue
Magnitude of the Residue
860.1400
Potable water
NR
[CR]
NR
NR
TGAI
1,12
860.1400
Fish
NR
[CR]
NR
NR
TGAI
1,13
860.1400
Irrigated crops
NR
[CR]
NR
NR
TGAI
1,14
860.1460
Food handling
NR
NR
NR
[CR]
TGAI
1,15
860.1480
Meat/milk/poultry/eggs
[CR]
[CR]
[CR]
[CR]
TGAI or plant
metabolites
1,7,8,10
860.1500
Crop field trials
[CR]
[CR]
[CR]
[CR]
TGAI
1,3,4
860.1520
Processed food/feed
[CR]
[CR]
[CR]
[CR]
TGAI
1,16
860.1540
Anticipated residues
[CR]
[CR]
[CR]
[CR]
Residue of concern
1,10,17
860.1550
Proposed tolerances
[CR]
[CR]
[CR]
[CR]
Residue of concern
1,18
860.1560
Reasonable grounds in
support of the petition
[CR]
[CR]
[CR]
[CR]
Residue of concern
1,10
860.1650
Submittal of analytical reference standards
[CR]
[CR]
[CR]
[CR]
TGAI
10,19
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(e) Test notes. The following test
notes are applicable to the data
requirements for biochemical residue
for specific uses as referenced in the last
column of the table contained in
paragraph (d) of this section.
1. Residue chemistry data requirements
apply to biochemical pesticide products
when Tier II or Tier III toxicology data are
required, as specified for biochemical agents
in the biochemical human health assessment
data requirements, § 158.950.
2. The same chemical identity data are
required for biochemical product chemistry
data requirements,§ 158.930 with an
emphasis on impurities.
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3. Required information includes crops to
be treated, rate of application, number and
timing of applications, preharvest intervals,
and relevant restrictions.
4. Residue data for outdoor residential uses
are required if home gardens are to be treated
and the home garden use pattern is different
from use patterns where tolerances have been
established.
5. Required unless it is an arthropod
pheromone applied at a rate less than or
equal to 150 grams active ingredient per acre.
6. Required for indoor uses where the
pesticide is applied directly to food, in order
to determine metabolites and/or degradates.
7. Data on metabolism in livestock are
required when residues occur on a livestock
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feed or if the pesticide is to be applied
directly to livestock. If results from the plant
metabolism study show differing metabolites
in plants from those found in animals, an
additional livestock metabolism study
involving dosing with the plant metabolite(s)
may also be required.
8. Livestock feeding studies are required
whenever a pesticide residue is present in
livestock feed or when direct application to
livestock uses occurs.
9. A residue method suitable for
enforcement of tolerances is required
whenever a numeric tolerance is proposed.
10. Required for indoor uses if the indoor
use could result in pesticide residues in or
on food or feed.
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11. Data are required to determine whether
FDA/USDA multiresidue methodology
would detect and identify the pesticides and
any metabolites.
12. Data on residues in potable water are
required whenever a pesticide is to be
applied directly to water, unless it can be
determined that the treated water would not
be used (eventually) for drinking purposes,
by man or animals.
13. Data on residues in fish are required
whenever a pesticide is to be applied directly
to water inhabited, or that will be inhabited,
by fish that may be caught or harvested for
human consumption.
14. Data on residues in irrigated crops are
required when a pesticide is to be applied
directly to water that could be used for
irrigation or to irrigation facilities such as
irrigation ditches.
15. Data on residues in food/feed in food
handling establishments are required
whenever a pesticide is to be used in food/
feed handling establishments.
16. Data on the nature and level of residue
in processed food/feed are required when
detectible residues could concentrate on
processing.
17. Anticipated residue data are required
when the assumption of tolerance level
residues would result in predicted exposure
at an unsafe level of exposure. Data on the
level or residue in food as consumed would
be used to obtain a more precise estimate of
potential dietary exposure.
18. The proposed tolerance must reflect the
maximum residue likely to occur in crops in
meat, milk, poultry, or eggs.
19. Required when a residue analytical
method is required.
§ 158.950 Human healthassessment data
dequirements table.
(a) General. (1) Sections 158.100
through 158.130 describe how to use
this table to determine the human
health assessment data requirements for
a particular pesticide product.
(2) The data in this section (158.950)
are not required for straight chain
lepidopteran pheromones when applied
up to a maximum use rate of 150 grams
active ingredient/acre/year.
(b) Use patterns. (1) Food use
patterns, in general, include products
classified under the following general
uses: terrestrial food crop use; terrestrial
feed crop use; aquatic food crop use;
greenhouse food crop use.
(2) Nonfood use patterns include
products classified under the general
use patterns of terrestrial nonfood crop
use; aquatic nonfood residential use;
aquatic nonfood outdoor use; aquatic
nonfood industrial use; greenhouse
nonfood crop use; forestry use;
residential outdoor use; residential
indoor use; indoor food use; indoor
nonfood use; indoor medical use.
(c) Key. R=Required; [R]=Required for
registrations and experimental use
permits; CR=Conditionally required;
[CR]=Conditionally required for
registrations and experimental use
permits; NR=Not required;
MP=Manufacturing-use product;
EP=End-use product; TEP=Typical enduse product; TGAI=Technical grade of
the active ingredient; Residue of
concern= the active ingredient and its
metabolites, degradates, and impurities
of toxicological concern; All= all of the
above. Specific conditions,
qualifications, or exceptions to the
designated test procedures appear in
paragraph (e) of this section, and apply
to the individual tests in the following
table:
(d) Table. The following table shows
the data requirements for biochemical
human health assessment. The test
notes are shown in paragraph (e) of this
section.
TABLE—BIOCHEMICAL HUMAN HEALTH ASSESSMENT DATA REQUIREMENTS
Use Patterns
Guideline Number
Test substance to support
Data Requirement
Test notes
Food
Nonfood
MP
EP
Tier I
Acute Testing
870.1100
Acute oral toxicity-rat
[R]
[R]
TGAI and
MP≤
TGAI and EP
1
870.1200
Acute dermal toxicity
[R]
[R]
TGAI and
MP
TGAI and EP
1,2
870.1300
Acute inhalation toxicity—rat
[R]
[R]
TGAI and
MP
TGAI and EP
3
870.2400
Primary eye irritation—
rabbit
[R]
[R]
TGAI and
MP
TGAI and EP
2
870.2500
Primary dermal irritation
[R]
[R]
TGAI and
MP
TGAI and EP
1,2
870.2600
Dermal sensitization
R
R
TGAI and
MP
TGAI and EP
2,4
none
Hypersensitivity incidents
[R]
[R]
All
All
5
870.3100
90-day oral (one species)
[R]
CR
TGAI
TGAI
6
870.3250
90-day dermal—rat
CR
CR
TGAI
TGAI
7
870.3465
90-day inhalation—rat
CR
CR
TGAI
TGAI
8
erjones on PROD1PC68 with PROPOSALS2
Subchronic Testing
Developmental Toxicity
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TABLE—BIOCHEMICAL HUMAN HEALTH ASSESSMENT DATA REQUIREMENTS—Continued
Use Patterns
Guideline Number
Test substance to support
Data Requirement
Test notes
Food
Nonfood
MP
EP
Prenatal developmental—rat preferably
[R]
[CR]
TGAI
TGAI
9
870.5100
Bacterial reverse mutation test
[R]
[CR]
TGAI
TGAI
10
870.5300
In vitro mammalian cell
gene mutation test
[R]
[CR]
TGAI
TGAI
10,11
870.3700
Mutagenicity Testing
Tier II
Mutagenicity Testing (In vivo cytogenetics)
870.5385
Mammalian bone marrow chromosomal aberration
CR
CR
TGAI
TGAI
13
870.5395
Mammalian erythrrocyte
micronucleus
CR
CR
TGAI
TGAI
13
Prenatal developmental
[CR]
[CR]
TGAI
TGAI
9
Immunotoxicity
CR
CR
TGAI
TGAI
12,13
875.1000
Background for application exposure monitoring test guidelines
CR
CR
TGAI
TGAI
15
875.1100
Dermal outdoor exposure
CR
CR
TGAI
TGAI
15
875.1200
Dermal indoor exposure
CR
CR
TGAI
TGAI
15
875.1300
Inhalation outdoor exposure
CR
CR
TGAI
TGAI
15
875.1400
Inhalation indoor exposure
CR
CR
TGAI
TGAI
15
875.1500
Biological monitoring
CR
CR
TGAI
TGAI
15
875.1700
Product use information
[R]
[R]
TGAI
TGAI
—
Developmental Toxicity
870.3700
Special Tests
880.3550
Applicator/User Exposure
Tier III
Chronic Testing/Special Testing
Immune response
CR
CR
TGAI
TGAI
14
870.3800
erjones on PROD1PC68 with PROPOSALS2
880.3800
Reproduction and fertility effects
CR
CR
TGAI
TGAI
16
870.4100
Chronic oral—rodent
and nonrodent
CR
CR
TGAI
TGAI
17
870.4200
Carcinogenicity—two
species—rat and
mouse preferred
CR
CR
TGAI
TGAI
18
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TABLE—BIOCHEMICAL HUMAN HEALTH ASSESSMENT DATA REQUIREMENTS—Continued
Use Patterns
Guideline Number
Test substance to support
Data Requirement
Test notes
Food
MP
EP
Mammalian
spermatogonial chromosome aberration
test
CR
CR
TGAI
TGAI
19
Companion animal
safety
870.5380
Nonfood
CR
CR
Choice
Choice
20
Special Testing
870.7200
(e) Test notes. The following test
notes are applicable to the data
requirements for biochemical human
health assessment as referenced in the
last column of the table in paragraph (d)
of this section.
1. Required unless the test material is a gas
or highly volatile (vapor pressure
>104torr).
P≤2. Required unless the test material is
corrosive to skin or has pH <2 or >11.5.
3. Required when the pesticide, under
conditions of use, would result in respirable
material (e.g., gas, volatile substance or
aerosol/particulate), unless it is a straight
chain lepidopteran pheromone.
4. Required if repeated contact with human
skin is likely to occur under conditions of
use.
erjones on PROD1PC68 with PROPOSALS2
5. Hypersensitivity incidents must be
reported as adverse effects data.
6. Required for non-food uses that are
likely to result in repeated oral exposure to
humans.
7. Required to support uses involving
purposeful application to the human skin or
which would result in comparable prolonged
human exposure to the product (e.g., insect
repellents) and if any of the following criteria
are met:
(i) Data from a 90–day oral study are not
required.
(ii) The active ingredient is known or
expected to be metabolized differently by the
dermal route of exposure than by the oral
route and the metabolite is of toxicological
concern.
(iii) The use pattern is such that the dermal
route would be the primary route of
exposure.
8. Required if there is a likelihood of
significant levels of repeated inhalation
exposure to the pesticide as a gas, vapor, or
aerosol.
9. Required if the use of the product under
widespread and commonly recognized
practice may reasonably be expected to result
in significant exposure to female humans
(e.g., occupational exposure or repeated
application of insect repellents directly to the
skin). Tier II data is required on a different
test species from Tier I data when
developmental effects are observed in the
first study and information on species-tospecies extrapolation is needed.
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10. It is required to support nonfood uses
if either (i) the use is likely to result in
significant human exposure; or (ii) if the
active ingredient (or its metabolites) is
structurally related to a known mutagen or
belongs to any chemical class of compounds
containing a known mutagen. Additional
mutagenicity tests that may have been
performed plus a complete reference list
must also be submitted. Subsequent testing
may be required based on the available
evidence.
11. Choice of assay using either (1) mouse
lymphoma L5178Y cells, thymidine kinase
(tk) gene locus, maximizing assay conditions
for small colony expression or detection; (2)
Chinese hamster ovary (CHO) or Chinese
hamster lung fibroblast (V79) cells,
hypoxanthine-guanine phosphoribosyl
transferase (hgprt) gene locus, accompanied
by an appropriate in vivo test for
clastogenicity; or (3) CHO cells strains AS52,
xanthine-guanine phosphoribosyl transferase
(xprt) gene locus.
12. Required if there are effects on
hematology, clinical chemistry, lymphoid
organ weights and histopathology are
observed in the 90–day studies.
13. Required if results from the Tier I
mutagenicity tests are positive. Allowed
choice of assays, initial considerations
usually given to rodent bone marrow, using
either metaphase analysis (aberrations) or
micronucleus assay.
14. Required if adverse effects are observed
in the Tier II immunotoxicity study. The
protocol for evaluating adverse effects to the
immune response should be developed after
evaluating the effects noted in the
immunotoxicity study.
15. These data are required when any
human health effects assessment data
indicate that the biochemical may pose a
potential hazard to the applicator/user. It is
recommended that the Agency be consulted
prior to study initiation to determine what
studies are appropriate based on the nature
of the adverse effects seen in the human
health assessment data and the available
exposure data. Studies performed to support
registration of insect repellents may require
modifications to these guidelines.
16. Required if there is evidence of: (a)
endocrinological effects from the subchronic
toxicity studies, (b) developmental effects in
the prenatal developmental toxicity study(s),
or (c) genotoxicity to mammals based on
results from the mutagenicity tests. The use
of a combined study that utilizes the two-
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generation reproduction study in rodents
(guideline 870.3800) as a basic protocol for
the addition of other endpoints or functional
assessments in the immature animal is
encouraged.
17. Required if the potential for adverse
chronic effects is indicated based on any of
the following:
(i) The subchronic effect level established
in the following Tier I studies: 90–day
feeding toxicity study, the 90–day dermal
toxicity study, or the 90–day inhalation
toxicity study.
(ii) The pesticide use pattern (e.g., rate,
frequency, and site of application).
(iii) The frequency and level of repeated
human exposure that is expected.
18. Required if the product meets either of
the following criteria:
(i) The active ingredient (or any of its
metabolites, degradation products, or
impurities) produce(s) in Tier I subchronic
studies a morphologic effect (e.g.,
hyperplasia or metaplasia) in any organ that
potentially could lead to neoplastic change.
(ii) Adverse cellular effects suggesting
carcinogenic potential are observed in Tier II
immunotoxicity and Tier III immune
response study or in Tier II mammalian
mutagenicity assays.
In addition, a 90–day range finding study
in both rats and mice is required to
determine the dose levels if carcinogenicity
studies are required. If the mouse
carcinogenicity study is not required, the 90–
day mouse subchronic study is likewise not
required.
19. Required if results from lower tiered
mutation or reproductive studies indicate
there is potential for chromosomal aberration
to occur.
20. May be required if the product’s use
will result in exposure to domestic animals
through, but not limited to, direct application
or consumption of treated feed.
§ 158.960 Nontarget organismsand
environmental fate data requirements table.
(a) General. (1) Sections 158.100
through 158.130 describe how to use
this table to determine the terrestrial
and aquatic nontarget organisms and
fate data requirements for a particular
pesticide product. Notes that apply to
an individual test including specific
conditions, qualifications, or exceptions
to the designated test are listed in
paragraph (e) of this section. In general,
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for all outdoor end-use products
including turf, the following studies are
required: one avian acute oral, one avian
dietary, one acute freshwater fish, one
acute freshwater invertebrate study,
plant toxicity testing and a honeybee
acute contact study.
(2) The data in this section are not
required for arthropod pheromones
when applied at up to a maximum use
rate of 150 grams active ingredient/acre/
year except when the product is
expected to be available to avian species
(i.e., granular formulation).
(b) Use patterns. The terrestrial use
pattern includes products classified
under the general use patterns of
terrestrial food crop, terrestrial feed
crop, and terrestrial nonfood/nonfeed
MP=Manufacturing-use product;
EP=End-use product; TEP=Typical enduse product; TGAI=Technical grade of
the active ingredient; Residue of
concern= the active ingredient and its
metabolites, degradates, and impurities
of toxicological concern; All= all of the
above. Specific conditions,
qualifications, or exceptions to the
designated test procedures appear in
paragraph (e) of this section, and apply
to the individual tests in the following
table:
(d) Table. The following table shows
the data requirements for biochemical
nontarget organisms and environmental
fate. The test notes are shown in
paragraph (e) of this section.
crop. The greenhouse use pattern
includes products classified under the
general use patterns of greenhouse food
crop and greenhouse nonfood crop. The
indoor use pattern includes products
classified under the general use patterns
of indoor food and nonfood use. The
remaining terrestrial uses include:
forestry and residential outdoor use.
Data are also required for the general
use patterns of aquatic food and
nonfood crop use.
(c) Key. R=Required; [R]=Required for
registrations and experimental use
permits; CR=Conditionally required;
[CR]=Conditionally required for
registrations and experimental use
permits; NR=Not required;
TABLE—BIOCHEMICAL NONTARGET ORGANISMS AND ENVIRONMENTAL FATE DATA REQUIREMENTS
Use Groups containing data requirements
Data Requirement
Terrestrial
Aquatic
Greenhouse
Food/feed,
nonfood
Guideline Number
Food,
nonfood
Food,
nonfood
Forestry,
residential outdoor
Indoor
Test Substance
Test notes
Food,
nonfood
Tier I
Avian Testing
850.2100
Avian acute oral toxicity
[R]
[R]
CR
[R]
CR
TGAI, EP
1,2,3,4
850.2200
Avian dietary toxicity
[R]
[R]
CR
[R]
CR
TGAI, EP
1,2,3,4
Aquatic Organism Testing
850.1075
Fish acute toxicity,
freshwater
[R]
[R]
CR
[R]
CR
TGAI, EP
2,3,4,5
850.1010
Aquatic invertebrate
acute toxicity, freshwater
[R]
[R]
CR
[R]
CR
TGAI, EP
2,3,4,5
850.4100
Terrestrial Plant Toxicity, Seedling emergence
R
R
NR
R
NR
TGAI, EP
5
850.4150
Terrestrial Plant Toxicity, Vegetative vigor
R
R
NR
R
NR
TGAI, EP
5
Nontarget Insect Testing
R
R
R
R
NR
TGAI
14
Nontarget Plant Testing
Insect Testing
880.4350
Tier II
Environmental Fate Testing
erjones on PROD1PC68 with PROPOSALS2
163-1 (835.1230)
Sediment and soil adsorption/desorption
for parent and
degradates
CR
CR
CR
CR
NR
TGAI
6
163-1 (835.1240)
Soil column leaching
CR
CR
CR
CR
NR
TGAI
6
163-2 (835.1410)
Laboratory volatilization
from soil
CR
NR
CR
CR
NR
TEP
7
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TABLE—BIOCHEMICAL NONTARGET ORGANISMS AND ENVIRONMENTAL FATE DATA REQUIREMENTS—Continued
Use Groups containing data requirements
Data Requirement
Terrestrial
Aquatic
Greenhouse
Food/feed,
nonfood
Guideline Number
Food,
nonfood
Food,
nonfood
Forestry,
residential outdoor
Indoor
Test Substance
Test notes
Food,
nonfood
161-1 (835.2120)
Hydrolysis
CR
CR
CR
CR
NR
TGAI
6
161-1 (835.4100)
Aerobic soil metabolism
CR
NR
CR
CR
NR
TGAI
6
161-2 (835.2240)
Photodegradation in
water
CR
CR
CR
CR
NR
TGAI
6
161-3 (835.2410)
Photodegradation on
soil
CR
NR
CR
CR
NR
TGAI
6
162-2 (835.4200)
Anerobic soil metabolism
CR
NR
NR
NR
NR
TGAI
6
162-4 (835.4300)
Aerobic aquatic metabolism
CR
CR
CR
CR
NR
TGAI
6
162-3(835.4400)
Anerobic aquatic metabolism
CR
CR
NR
NR
NR
TGAI
6
880.4425
Dispenser -water
leaching
CR
NR
CR
CR
NR
EP
8
850.4225
Seedling emergence
R
R
NR
R
NR
TGAI
9
850.4250
Vegetative vigor
R
R
NR
R
NR
TGAI
9
Nontarget Plant
Tier III
Aquatic Fauna Chronic, Life Cycle, and Field Studies
850.1300
850.1400
850.1500
Freshwater fish/ invertebrate testing
CR
CR
NR
CR
NR
TGAI
10
850.1025
850.1035
850.1045
850.1055
850.1350
850.1400
850.1500
Marine/Estuarine fish/
invertebrate animal
testing
CR
CR
NR
CR
NR
TGAI
10
850.1950
Aquatic field fish/
invertebratetesting
CR
CR
NR
CR
NR
EP
10
850.2300
Avian Reproduction
CR
CR
NR
CR
NR
TGAI
11
850.2400
Wild mammal acute
toxicity
CR
CR
NR
CR
NR
TGAI
11
850.2500
Terrestrial field testing
CR
CR
NR
CR
NR
EP
11
Field testing for Pollinators
CR
CR
NR
CR
NR
TEP
12
Terrestrial Wildlife
erjones on PROD1PC68 with PROPOSALS2
Beneficial Insects
850.3040
Nontarget Plants
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TABLE—BIOCHEMICAL NONTARGET ORGANISMS AND ENVIRONMENTAL FATE DATA REQUIREMENTS—Continued
Use Groups containing data requirements
850.4225
850.4250
850.4300
850.4450
Nontarget plant
erjones on PROD1PC68 with PROPOSALS2
1. Required for the EP when any end-use
formulation may contain other ingredients
that may be toxic to nontarget organisms or
to support arthropod pheromones that would
be available to avian wildlife, (e.g., a granular
product).
2. Tests for pesticides intended solely for
indoor application would be required on a
case-by-case basis, depending on use pattern,
physical/chemical properties, production
volume, and other pertinent factors.
3. Not required for any use groups if the
pesticide is highly volatile (estimated
volatility >5 X 10-5 atm m3/mol).
4. Preferred test species are bobwhite quail,
mallard, or redwing blackbird for avian acute
oral toxicity studies; bobwhite quail or
mallard for avian dietary studies, rainbow
trout for acute freshwater fish studies; and
Daphnia magna for acute freshwater
invertebrate studies.
5. Required for the EP when the end-use
formulation may contain other ingredients
that may be toxic to nontarget organisms.
6. Required on a case-by-case basis when
results from Tier I studies indicate adverse
effects.
7. Required when results of any one or
more of the nontarget organism studies in
Tier I indicate potential adverse effects on
nontarget organisms and the pesticide is to be
applied on land.
8. Required when results of any one or
more of the nontarget organism studies in
Tier I indicate potential adverse effects on
nontarget organisms and the pesticide is to be
applied in a passive dispenser.
9. Required to support registration of
known phytotoxicants, i.e. herbicides,
desiccants, defoliants, and plant growth
regulators.
10. Required if environmental fate
characteristics indicate that the estimated
environmental concentration of the pesticide
in the aquatic environment is >0.01 of any
EC50 or LC50 determined in the aquatic
nontarget organism testing.
11. Required if either of the following
criteria are met:
(i) Environmental fate characteristics
indicate that the estimated concentration of
the pesticide in the terrestrial environment is
15:51 Mar 07, 2006
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Aquatic
Greenhouse
Food,
nonfood
CR
Data Requirement
(e) Test notes. The following test
notes are applicable to the data
requirements for biochemical nontarget
organisms and environmental fate as
referenced in the last column of the
table contained in paragraph (d) of this
section.
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Terrestrial
Food/feed,
nonfood
Guideline Number
CR
Food,
nonfood
Forestry,
residential outdoor
Food,
nonfood
NR
CR
NR
>0.20 the avian dietary LC50 or equal to or
>0.20 the avian oral single dose LD50
(converted to ppm).
(ii) The pesticide or any of its metabolites
or degradation products are stable in the
environment to the extent that potentially
toxic amounts may persist in the avian or
mammalian feed.
12. Required when results of Tier I
nontarget organism studies indicate potential
adverse effects on nontarget insects and
results of Tier II tests indicate exposure of
nontarget insects. Additional insect species
may have to be tested if necessary to address
issues raised by use patterns and potential
exposure of important nontarget insect
species, (e.g., threatened or endangered
species).
13. Required if the product is expected to
be transported from the site of application by
air, soil, or water. The extent of movement
would be determined by the results of the
Tier II environmental fate studies.
14. Required depending on pesticide mode
of action, method and timing of application,
and results of any available efficacy data.
Typically the honeybee acute toxicity
guideline (guideline 850.3020) satisfies this
requirement, however additional nontarget
insect species may have to be tested if
necessary to address issues raised by use
patterns and potential exposure of important
nontarget insect species, e.g., endangered
species.
§ 158.970 Biochemicalpesticides product
performance data requirements.
Product performance data must be
developed for all biochemical
pesticides. However, the Agency
typically does not require applicants to
submit such efficacy data unless the
pesticide product bears a claim to
control public health pests, such as pest
microorganisms infectious to man in
any area of the inanimate environment
or a claim to control vertebrates
(including but not limited to: rodents,
birds, bats, canids, and skunks) or
invertebrates (including but not limited
to: mosquitoes and ticks) that may
directly or indirectly transmit diseases
to humans. However, each registrant
must ensure through testing that his
products are efficacious when used in
accordance with label directions and
commonly accepted pest control
practices. The Agency reserves the right
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Indoor
Test Substance
Test notes
TGAI
13
to require, on a case-by-case basis,
submission of efficacy data for any
pesticide product registered or proposed
for registration.
Subpart M—Microbial Pesticides
§ 158.1000
Definition andApplicability.
(a) This subpart applies to all living
or dead microbial pesticides as
described in paragraphs (b) and (c) of
this section.
(b) Definition. Microbial pesticide is a
microorganism intended for preventing,
destroying, repelling, or mitigating any
pest, or intended for use as a plant
regulator, defoliant, or desiccant, that:
(1) Is a eucaryotic microorganism
including, but not limited to, protozoa,
algae, and fungi;
(2) Is a procaryotic microorganism,
including, but not limited to, bacteria;
or
(3) Is an autonomous replicating
microscopic element, including, but not
limited to, viruses.
(c) Applicability. (1) In addition to the
definition above, the definitions in
§ 158.3 also apply to this subpart.
(2) Each new isolate of a microbial
pesticide is treated as a new strain and
must be registered independently of any
similar registered microbial pesticide
strain and supported by data required in
this subpart.
(3) Genetically modified microbial
pesticides, may be subject to additional
data or information requirements on a
case-by-case basis depending on the
particular microorganism and/or its
parent microorganism(s), the proposed
pesticide use pattern, and the manner
and extent to which theorganism has
been genetically modified. Additional
requirements may be required on a caseby-case basis.
(4) Pest control organisms such as
insect predators, nematodes, and
macroscopic parasites are exempt from
the requirements of FIFRA as authorized
by section 25(b) of FIFRA and specified
in § 152.20 (a) of this chapter.
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§ 158.1010 Microbial pesticidedata
requirements.
(a) For all microbial pesticides. (1)
The following § § 158.1010 through
158.1050 identify the data requirements
that are required to support registration
of microbial pesticides. The variations
in the test conditions are identified
within the test notes.
(2) Each data table includes ‘‘use
patterns’’ under which the individual
data are required, with variations
including all use patterns, food and
nonfood uses for terrestrial and aquatic
applications, greenhouse, indoor,
forestry, and residential outdoor
applications under certain
circumstances.
(3) The categories for each data
requirement are ‘‘R’’, which stands for
required, and ‘‘CR’’ which stands for
conditionally required. If a bracket
appears around the R or CR, the data are
required for both the registration and
experimental use permit requests.
Generally, ‘‘R’’ indicates that the data
are more likely required than for those
data requirements with CR. However, in
each case, the regulatory text preceding
the data table and the test notes
following the data table must be used to
determine whether the data requirement
must be satisfied.
(4) Each table identifies the test
substance that is required to be tested to
satisfy the data requirement. Test
substances may include: technical grade
active ingredient (TGAI),
manufacturing-use product (MP), enduse product (EP), typical end-use
product (TEP), residue of concern, and
pure active ingredient (PAI) or (All)
indicating all of the above. Commas
between the test substances (i.e., TGAI,
EP) indicate that data may be required
on the TGAI or EP or both depending on
the conditions set forth in the test note.
Data requirements which list two test
substances (i.e., TGAI and EP) indicate
that both are required to be tested. Data
requirements that list only the
manufacturing product (MP) as the test
substance apply to products containing
solely the technical grade of the active
ingredient and manufacturing-use
products to which other ingredients
have been intentionally added. Data
requirements listing the EP as the test
substance apply to any EP with an
ingredient in the end-use formulation
other than the active ingredient that is
expected to enhance the toxicity of the
product.
(b) Additional data requirements for
genetically modified microbial
pesticides. Additional requirements for
genetically modified microbial
pesticides may include but are not
limited to: genetic engineering
techniques used; the identity of the
inserted or deleted gene segment (base
sequence data or enzyme restriction
map of the gene); information on the
control region of the gene in question;
a description of the ‘‘new’’ traits or
characteristics that are intended to be
expressed; tests to evaluate genetic
stability and exchange; and selected
Tier II environmental expression and
toxicology tests.
§ 158.1020 Product analysisdata
requirements table.
(a) General. Sections 158.100 through
158.130 describe how to use this table
to determine the product analysis data
requirements and the substance to be
tested for a particular microbial
pesticide. Specific conditions,
qualifications, or exceptions to the
designated test are identified in (d) of
this section, and the test notes appear in
paragraph (e) of this section.
(b) Key. R=Required; [R]=Required for
registrations andexperimental use
permits; CR=Conditionally required;
[CR]=Conditionally required for
registrations and experimental use
permits; NR=Not required;
MP=Manufacturing-use product;
EP=End-use product; TEP=Typical enduse product; TGAI=Technical grade of
the active ingredient; All= all of the
above. Specific conditions,
qualifications, or exceptions to the
designated test procedures appear in
paragraph (e) of this section, and apply
to the individual tests in the following
table:
(c) Table. The following table shows
the data requirements for microbial
product analysis. The test notes are
shown in paragraph (d) of this section.
TABLE—MICROBIAL PRODUCT ANALYSIS DATA REQUIREMENTS
All Use patterns
Guideline Number
Test substances to support
Data Requirement
Test notes
Food Use
Nonfood Use
MP
EP
Product Chemistry and Composition
885.1100
Product Identity
[R]
[R]
MP
EP
—
885.1200
Manufacturing process
[R]
[R]
TGAI and
MP
TGAI and EP
1,2
Deposition of a sample
in a nationally recognized culture collection
[R]
[R]
TGAI
TGAI
—
Discussion of formation
of unintentional ingredients
[R]
[R]
TGAI and
MP
TGAI and EP
2
885.1300
Analysis and Certified Limits
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885.1400
Analysis of samples
[R]
[R]
TGAI and
MP
TGAI and EP
2,3
885.1500
Certification of limits
[R]
R
MP
EP
—
[R]
[R]
TGAI
TGAI
—
Physical and Chemical Characteristics
830.6302
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TABLE—MICROBIAL PRODUCT ANALYSIS DATA REQUIREMENTS—Continued
All Use patterns
Guideline Number
Test substances to support
Data Requirement
Test notes
Food Use
Nonfood Use
MP
EP
830.6303
Physical state
[R]
[R]
TGAI
TGAI
—
830.6304
Odor
[R]
[R]
TGAI
TGAI
—
830.6313
Stability to normal and
elevated temperatures, metals and
metal ions
[R]
[R]
TGAI
TGAI
—
830.6317
Storage stability
[R]
[R]
TGAI and
MP
TGAI and EP
—
830.6319
Miscibility
[R]
[R]
MP
EP
4
830.6320
Corrosion Characteristics
[R]
[R]
MP
EP
5
830.7000
pH
[R]
[R]
TGAI
TGAI
—
830.7100
Viscosity
[R]
[R]
MP
EP
6
830.7300
Density/relative density/
bulk density (specific
gravity)
[R]
[R]
TGAI
TGAI
—
(d) Test notes. The following test notes are
applicable to the data requirements for
microbial product analysis as referenced in
the last column of the table contained in
paragraph (c) of this section.
1. If an experimental use permit is being
sought, and if the pesticide is not already
under full-scale production, a schematic
diagram and/or description of the
manufacturing process suffices.
2. If an experimental use permit is being
sought, and if the product is not already
under full-scale production, a discussion of
unintentional ingredients is required to be
submitted to the extent this information is
available.
experimental use permit. For full registration,
generally an analysis of samples is a
compilation of batches, over a period of time,
depending on the frequency of
manufacturing.
3. Required to support registration of each
manufacturing-use product and end-use
product. This analysis must be conducted at
the point in the production process after
which there would be no potential for
microbial contamination or microbial
regrowth. For pesticides in the production
stage, a preliminary product analytical
method and data would suffice to support an
(a) General. Sections 158.100 through
158.130 describe how to use this table
to determine the residue chemistry data
requirements and the substance to be
tested for a particular microbial
pesticide. Specific conditions,
qualifications, or exceptions to the
designated test appear in (d) of this
4. Only required for emulsifiable liquid
forms of microbial pesticides.
5. Required when microbial pesticides are
packaged in metal, plastic, or paper
containers.
6. Only required for liquid forms of
microbial pesticides.
§ 158.1030
table.
Residue datarequirements
section, and the procedures appear in
paragraph (e) of this section.
(b) Key. R=Required; [R]=Required for
registrations and experimental use
permits; CR=Conditionally required;
[CR]=Conditionally required for
registrations and experimental use
permits; NR=Not required;
MP=Manufacturing-use product;
EP=End-use product; TEP=Typical enduse product; TGAI=Technical grade of
the active ingredient; All= all of the
above. Specific conditions,
qualifications, or exceptions to the
designated test procedures appear in
paragraph (d) of this section, and apply
to the individual tests in the following
table:
(c) Table. The following table shows
the data requirements for microbial
residue. The test notes are shown in
paragraph (d) of this section.
TABLE—MICROBIAL RESIDUE DATA REQUIREMENTS
Data Requirement
All Use Patterns
Test Substance Data to
support MP or
EP
Test notes
885.2000
Background for Residue analysis of microbial
pest control agents
[CR]
EP
1
885.2100
Chemical Identity
[CR]
EP
1
885.2200
Nature of the Residue in plants
[CR]
EP
1
885.2250
Nature of the Residue in animals
[CR]
EP
1
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Guideline Number
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TABLE—MICROBIAL RESIDUE DATA REQUIREMENTS—Continued
Guideline Number
All Use Patterns
Data Requirement
Test Substance Data to
support MP or
EP
Test notes
885.2300
Analytical methods—plants
[CR]
TGAI
1
885.2350
Analytical methods-animals
[CR]
TGAI
1
885.2400
Storage Stability
[CR]
EP
1
885.2500
Magnitude of residue in plants
[CR]
EP
1
885.2550
Magnitude of residues in meat, milk, poultry,
eggs
[CR]
EP
1
885.2600
Magnitude of residues in potable water, fish,
and irrigated crops
[CR]
EP
1
(d) Test notes. The following test note
is applicable to the data requirements
for microbial residue as referenced in
the last column of the table contained in
paragraph (c) of this section.
conditions, qualifications, or exceptions
to the designated test are listed in
paragraph (e) of this section.
(b) Use patterns. (1) This category
includes products classified under the
following general uses: terrestrial food
and nonfood crop use; terrestrial feed
crop use; aquatic food and nonfood crop
use; greenhouse food and nonfood crop
use; forestry; residential outdoor and
indoor; and indoor food use.
(2) Nonfood use patterns include
products classified under the general
use patterns of terrestrial nonfood crop
use; aquatic nonfood residential use;
aquatic nonfood outdoor use; aquatic
nonfood industrial use; greenhouse
nonfood crop use; forestry use;
residential outdoor use; residential
indoor use; indoor food use; indoor
nonfood use.
1. Required when the results of testing:
i. Indicate the potential to cause adverse
human health effects or the product
characterization indicates the microbial
pesticide has a significant potential to
produce a mammalian toxin; andii. The use
pattern is such that residues may be present
in or on food or feed crops.
§ 158.1040
table.
Toxicology datarequirements
(a) General. Sections 158.100 through
158.130 describe how to use this table
to determine the toxicology data
requirements for a particular pesticide
product. Notes that apply to an
individual test and include specific
(c) Key. R=Required; [R]=Required for
registrations andexperimental use
permits; CR=Conditionally required;
[CR]=Conditionally required for
registrations and experimental use
permits; NR=Not required;
MP=Manufacturing-use product;
EP=End-use product; TEP=Typical enduse product; TGAI=Technical grade of
the active ingredient; All= all of the
above. Specific conditions,
qualifications, or exceptions to the
designated test procedures appear in
paragraph (e) of this section, and apply
to the individual tests in the following
table:
(d) Table. The following table shows
the data requirements for microbial
toxicology. The test notes are shown in
paragraph (e) of this section.
TABLE—MICROBIAL TOXICOLOGY DATA REQUIREMENTS
Guideline Number
All Use
patterns
Data Requirement
Test
substance
Test notes
Tier I
Acute oral toxicity/pathogenicity
[R]
TGAI
1
885.3150
Acute pulmonary toxicity/pathogenicity
[R]
TGAI
—
885.3200
Acute injection toxicity/pathogenicity/(intravenous)
Acute
injection
toxicity/pathogenicity
/(intraperitoneal)
[R]
TGAI
2
885.3400
Hypersensitivity incidents
[R]
All
3
885.3500
Cell culture
[R]
TGAI
4
870.1100
Acute oral toxicity
[R]
MP , EP
1,5
870.1200
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885.3050
Acute dermal toxicity
[R]
MP , EP
5
870.1300
Acute inhalation toxicity
[R]
MP , EP
5,7
870.2400
Acute eye irritation
[R]
MP , EP
5
870.2500
Primary dermal irritation
[CR]
MP , EP
5,6
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TABLE—MICROBIAL TOXICOLOGY DATA REQUIREMENTS—Continued
Guideline Number
All Use
patterns
Data Requirement
Test
substance
Test notes
Tier II
885.3550
Acute toxicology
CR
TGAI
8
885.3600
Subchronic toxicity/pathogenicity
CR
TGAI
9
885.3650
Reproductive fertility effects
CR
TGAI
10,14
870.4200
Carcinogenicity
CR
TGAI
11,14
870.7800
Immunotoxicity
CR
TGAI
12,14
885.3000
Infectivity/pathogenicity analysis
CR
TGAI
13,14
Tier III
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(e) Test notes. The following test
notes are applicable to the data
requirements for microbial toxicology as
referenced in the last column of the
table contained in paragraph (d) of this
section:
1. The acute oral toxicity/pathogenicity
study is required to support the TGAI.
However, it can be combined with the unit
dose portion of the acute oral toxicity study,
with an EP or MP test material to fulfill the
requirement for the TGAI and the MP or EP
in a single study, if the new protocol is
designed to address the endpoints of
concern.
2. Data not required for products whose
active ingredient is a virus. For test materials
whose size or consistency may prevent use
of an i.v. injection, the i.p. injection
procedure may be employed.
3. Hypersensitivity incidents for registered
products must be reported if they occur.
4. Data must be submitted only for
products whose active ingredient is a virus.
5. The 870 series studies for the MP and
EP are intended to provide data on the acute
toxicity of the product. Waivers for any or all
of these studies may be granted when the
applicant can demonstrate that the
combination of inert ingredients is not likely
to pose any significant human health risks.
Where appropriate, the limit dose approach
to testing is recommended.
6. Data are required only if dermal
irritation is found after dosing in acute
dermal toxicity study.
7. Required when the product consists of,
or under conditions of use would result in,
an inhalable material (e.g., gas, volatile
substances, or aerosol particulate).
8. Data required when significant toxicity,
in the absence of pathogenicity and
significant infectivity, is observed in acute
oral, injection, or pulmonary studies (Tier I).
Route(s) of exposure correspond to routes
where toxicity was observed in Tier I studies.
The toxic component of the TGAI is to be
tested.
9. Data required when significant
infectivity and/or unusual persistence is
observed in the absence of pathogenicity or
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toxicity in Tier I studies. Routes of exposure
(oral and/or pulmonary) correspond to routes
in Tier I studies where adverse effects were
noted. Data may also be required to evaluate
adverse effects due to microbial
contaminants or to toxic byproducts.
10. Data are required when any of the
following criteria are met:
(i) Significant infectivity of the microbial
pest control agent (MPCA) was observed in
test animals in the Tier II subchronic study
and in which no significant signs of toxicity
or pathogenicity were observed.
(ii) The microbial pesticide is a virus
which can persist or replicate in mammalian
cell culture lines.
(iii) The microbial pesticide is not
amenable to thorough taxonomic
classification, and is related to organisms
known to be parasitic for mammalian cells.
(iv) The microbial pesticide preparation is
not well purified, and may contain
contaminants which are parasitic for
mammals.
11. Data may be required for products
known to contain or suspected to contain
carcinogenic viruses or for microbial
components that are identified as having
significant toxicity in Tier II testing.
12. Data may be required for products
known to contain or suspected to contain
viruses that can interact in an adverse
manner with components of mammalian
immune system.
13. An analysis of human infectivity/
pathogenicity potential using scientific
literature, genomic analysis, and/or actual
specific cell culture/animal data may be
required for products known to contain or
suspected of containing intracellular
parasites of mammalian cells for products
that exhibit pathogenic characteristics in Tier
I and/or Tier II, for products which are
closely related to known human pathogens
based on the Product Analysis data, or for
known human pathogens that have been
‘‘disarmed’’ or rendered non-pathogenic for
humans.
14. Test standards may have to be modified
depending on the characteristics of the
microorganism. Requirements may vary for
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these studies depending on the active
ingredient being tested. Consultation with
the Agency is advised before performing
these Tier III studies.
§ 158.1050 Nontarget organismsand
environmental fate data requirements table.
(a) General. Sections 158.100 through
158.130 describe how to use this table
to determine the terrestrial and aquatic
nontarget organisms data requirements
for a particular microbial pesticide
product. Notes that apply to an
individual test including specific
conditions, qualifications, or exceptions
to the designated test are listed in
paragraph (e) of this section.
(b) Use patterns. Aquatic uses
include: food and feed, nonfood uses
(e.g., outdoor, residential, and
industrial). Terrestrial uses include:
Food, Feed, Non-Food, Forestry,
Residential outdoor, greenhouse (food
and food), Indoor (food and nonfood),
and Industrial.
(c) Key. R=Required; [R]=Required for
registrations and experimental use
permits; CR=Conditionally required;
[CR]=Conditionally required for
registrations and experimental use
permits; NR=Not required;
MP=Manufacturing-use product;
EP=End-use product; TEP=Typical enduse product; TGAI=Technical grade of
the active ingredient; All= all of the
above. Specific conditions,
qualifications, or exceptions to the
designated test procedures appear in
paragraph (e) of this section, and apply
to the individual tests in the following
table:
(d) Table. The following table shows
the data requirements for microbial
nontarget organisms and environmental
fate. The test notes are shown in
paragraph (e) of this section.
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TABLE—MICROBIAL NONTARGET ORGANISMS AND ENVIRONMENTAL FATE DATA REQUIREMENTS
Aquatic
Terrestrial
Non-Food
Guideline Number
Data Requirement
Food,
Feed
Out
door,Residential,
Industrial
Food,
Feed,
Nonfood
Forestry
Residential
outdoor
Greenhouse
Food,
NonFood
Indoor
Food,
NonFood
Industrial
Test
Substance
Test
notes
Tier I
885.4050
Avian oral
toxicity
R
[R]
[R]
[R]
[R]
CR
CR
CR
TGAI
1,2
885.4100
Avian inhalation toxicity/pathogenicity
CR
CR
CR
CR
CR
CR
CR
CR
TGAI
1,2,3
885.4150
Wild mammal toxicity/pathogenicity
CR
CR
CR
CR
CR
NR
NR
CR
TGAI
1,4
885.4200
Freshwater fish
toxicity/ pathogenicity
R
[R]
[R]
[R]
CR
CR
CR
CR
TGAI
1, 2,5
885.4240
Freshwater invertebrate toxicity/
pathogenicity
R
[R]
[R]
[R]
CR
CR
CR
CR
TGAI
1, 2,5
885.4280
Estuarine/Marine
fish testing
Estuarine and marine invertebrate
testing
CR
CR
CR
CR
CR
NR
NR
CR
TGAI
1,6
885.4300
Nontarget plant
testing
CR
CR
CR
[R]
CR
NR
CR
CR
TE
1,7
885.4340
Nontarget insect
testing
[R]
[R]
[R]
[R]
R
CR
NR
CR
TGAI
1,8
885.4380
Honey bee testing
[R]
[[R]
[R]
[R]
R
CR
NR
CR
TGAI
1
885.5200
Terrestrial environmental expression
tests
CR
CR
CR
CR
CR
NR
NR
CR
TGAI or
TEP
9
885.5300
Freshwater environmental expression
tests
CR
CR
CR
CR
CR
NR
NR
CR
TGAI or
TEP
10
885.5400
Marine or estuarine
environmental expression tests
CR
CR
CR
CR
CR
NR
NR
CR
TGAI or
TEP
11,12
885.4600
Avian chronic pathogenicity and reproduction test
CR
CR
CR
CR
CR
NR
NR
CR
TGAI
12, 13
885.4650
Aquatic invertebrate
range testing
CR
CR
CR
CR
CR
NR
NR
CR
TGAI
12, 14
885.4700
Fish life cycle studies
CR
CR
CR
CR
CR
NR
NR
CR
TGAI
12, 14/
ROW≤
885.4750
Aquatic ecosystem
test
CR
CR
CR
CR
CR
NR
NR
CR
TGAI
15
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Tier IV
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TABLE—MICROBIAL NONTARGET ORGANISMS AND ENVIRONMENTAL FATE DATA REQUIREMENTS—Continued
Aquatic
Terrestrial
Non-Food
Guideline Number
Data Requirement
Food,
Feed
Out
door,Residential,
Industrial
Food,
Feed,
Nonfood
Forestry
Residential
outdoor
Greenhouse
Food,
NonFood
Indoor
Food,
NonFood
Industrial
Test
Substance
Test
notes
850.2500
850.1950
Field testing for terrestrial wildlife
and Field testing
for aquatic organisms
CR
CR
CR
CR
CR
NR
NR
CR
TGAI or
TEP
11, 16
850.2500
Simulated or actual
field tests (birds,
mammals)
CR
CR
CR
CR
CR
NR
NR
CR
TEP
16, 17,
20
850.1950
Simulated or actual
field test (aquatic
organisms)
CR
CR
CR
CR
CR
NR
NR
CR
TEP
16, 18,
19, 20
850.2500
Simulated or actual
field tests (insect
predators,
parasites)
CR
CR
CR
CR
CR
NR
NR
CR
TEP
16,
18,19,
20
850.3040
Simulated or actual
field tests (insect
pollinators)
CR
CR
CR
CR
CR
NR
NR
CR
TEP
16,
18,19,
20
850.4300
Simulated or actual
field tests (plants)
CR
CR
CR
CR
CR
NR
NR
CR
TEP
16, 18,
19, 20
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(e) Test notes. The following test
notes are applicable to the data
requirements for microbial nontarget
organism and environmental fate as
referenced in the last column of the
table contained in paragraph (d) of this
section.
1. Tests for pesticides intended solely for
indoor application would be required on a
case-by-case basis, depending on use pattern,
production volume, and other pertinent
factors. Tests to support EUP’s are based on
the application timing and acreage.
2. The preferred species for the avian oral
study is either the bobwhite quail or mallard
duck. The preferred species for the avian
inhalation toxicity/pathogenicity study and
the avian chronic toxicity/pathogenicity
study is the bobwhite quail. There is also the
option to test the redwing black bird if there
is a concern for passerine species. The
rainbow trout is preferred for freshwater fish
testing. However, two species (rainbow trout
and bluegill sunfish are the preferred species)
must be tested for uses involving direct
freshwater exposure. Daphnia magna is the
preferred species for freshwater invertebrate
testing.
3. Data required when the nature of the
microbial pesticide and/or its toxins
indicates potential pathogenicity to birds.
4. Required on a case-by-case basis if
results of tests required by§ 158.1040 are
inadequate or inappropriate for assessment of
hazards to wild animals.
5. Required when there will be significant
exposure to aquatic organisms (fish and
invertebrates).
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6. Required if the product is intended for
direct application into the estuarine or
marine environment or expected to enter this
environment in significant concentrations
because of expected use or mobility pattern.
7. Required if the microbial pesticide is
taxonomically related to a known plant
pathogen.
8. Data are not required unless an active
microbial ingredient controls the target insect
pest by a mechanism of infectivity; i.e. may
create an epizootic condition in nontarget
insects.
9. Required if toxic or pathogenic effects
are observed in any of the following tests for
microbial pesticides:
(i) Avian acute oral or avian inhalation
studies.
(ii) Wild mammal studies.
(iii) Nontarget plant studies (terrestrial).
(iv) Honey bee studies.
(v) Nontarget insect studies.
10. Required when toxic or pathogenic
effects are observed in any of the following
Tier I tests for microbial pest control agents:
(i) Freshwater fish studies.
(ii) Freshwater aquatic invertebrate studies.
(iii) Nontarget plant studies (aquatic).
11. Required if product is applied on land
or in fresh water or marine/estuarine
environments and toxic or pathogenic effects
are observed in any of the following Tier I
tests for microbial pesticides:
(i) Estuarine and marine animal toxicity
and pathogenicity.
(ii) Plant studies—estuarine or marine
species.
12. An appropriate dose-response toxicity
test is required when toxic effects on
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nontarget terrestrial wildlife or aquatic
organisms (including plants) are reported in
one or more Tier I tests and results of Tier
II tests indicate exposure of the microbial
agent to the affected nontarget terrestrial
wildlife or aquatic organisms. The protocols
for these tests may have to be modified in
accordance with results from the nontarget
organism and environmental expression
studies.
13. Required when one or more of the
following are present:
(i) Pathogenic effects are observed in Tier
I avian studies.
(ii) Tier II environmental expression testing
indicate that long-term exposure of terrestrial
animals is likely.
14. Required when product is intended for
use in water or expected to be transported to
water from the intended use site, and when
pathogenicity or infectivity was observed in
Tier I aquatic studies.
15. Required if, after an analysis of the
microbial pesticide’s ability to survive and
multiply in the environment and what
ecological habitat it would occupy, the
intended use patterns, and the results of
previous nontarget organisms and
environmental expression tests, it is
determined that use of the microbial agent
may result in adverse effects on the nontarget
organisms in aquatic environments. Testing
is to determine if applications of the
microbial pest control would be expected to
disrupt the balance of populations in the
target ecosystem.
16. Tier IV studies may be conducted as a
condition of registration aspost-registration
monitoring if the potential for unreasonable
E:\FR\FM\08MRP2.SGM
08MRP2
Federal Register / Vol. 71, No. 45 / Wednesday, March 8, 2006 / Proposed Rule
erjones on PROD1PC68 with PROPOSALS2
adverse effects appears to be minimal during
that period of use due to implementation of
mitigation measures.
17. Required when both of the following
conditions occur:
(i) Pathogenic effects at actual or expected
field residue exposure levels are reported in
Tier III; and
(ii) The Agency determines that quarantine
methods would not prevent the microbial
pesticide from contaminating areas adjacent
to the test area.
18. Short term simulated or actual field
studies are required when it is determined
that the product is likely to cause adverse
short-term or acute effects, based on
consideration of available laboratory data,
use patterns, and exposure rates.
19. Data from a long-term simulated field
test (e.g., where reproduction and growth of
confined populations are observed) and/or an
actual field test (e.g., where reproduction and
growth of natural populations are observed)
are required if laboratory data indicate that
adverse long-term, cumulative, or life-cycle
effects may result from intended use.
20. Since test standards would be
developed on a case-by-case basis,
consultation with the Agency and
development of a protocol is advised before
performing these Tier IV studies.
VerDate Aug<31>2005
15:51 Mar 07, 2006
Jkt 205001
§ 158.1060 Microbial pesticidesproduct
performance data requirements.
Product performance data must be
developed for all microbial pesticides.
However, the Agency has waived all
requirements to submit efficacy data
unless the pesticide product bears a
claim to control public health pests,
such as pest microorganisms infectious
to man in any area of the inanimate
environment or a claim to control
vertebrates (including but not limited to:
rodents, birds, bats, canids, and skunks)
or invertebrates (including but not
limited to: mosquitoes and ticks) that
may directly or indirectly transmit
diseases to humans. However, each
registrant must ensure through testing
that his products are efficacious when
used in accordance with label directions
and commonly accepted pest control
practices. The Agency reserves the right
to require, on a case-by-case basis,
submission of efficacy data for any
pesticide product registered or proposed
for registration.
PO 00000
PART 172—[AMENDED]
5. The authority citation continues to
read as follows:
Authority: 7 U.S.C. 136c, 136w. Section
172.4 is also issued under 31 U.S.C. 9701.
6. In § 172.43 revise the definition for
‘‘microbial pesticide’’ to read as follows:
§ 172.43
Definitions.
*
*
*
*
*
Microbial pesticide means a
microorganism intended for preventing,
destroying repelling, or mitigating any
pest, or intended for use as a plant
regulator, defoliant, or desiccant, that:
(1) Is a eucaryotic microorganism
including, but not limited to, protozoa,
algae and fungi;
(2) Is a procaryotic microorganism,
including, but not limited to, bacteria;
or
(3) Is an autonomous replicating
microscopic element, including, but not
limited to, viruses.
*
*
*
*
*
[FR Doc. 06–2185 Filed 3–7–06; 8:45 am]
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Frm 00047
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Agencies
[Federal Register Volume 71, Number 45 (Wednesday, March 8, 2006)]
[Proposed Rules]
[Pages 12072-12117]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 06-2185]
[[Page 12071]]
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Part III
Environmental Protection Agency
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40 CFR Parts 158 and 172
Pesticides; Data Requirements for Biochemical and Microbial Pesticides;
Proposed Rule
Federal Register / Vol. 71, No. 45 / Wednesday, March 8, 2006 /
Proposed Rule
[[Page 12072]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 158 and 172
[EPA-HQ-OPP-2004-0415; FRL-7763-4]
RIN 2070-AD51
Pesticides; Data Requirements for Biochemical and Microbial
Pesticides
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: EPA is proposing to update and revise its data requirements
for the registration of microbial and biochemical pesticide products to
reflect current scientific knowledge. These proposed revisions are
intended to provide EPA with data and other information necessary to
support the registration of a biochemical and microbial pesticide
product, and will improve the Agency's ability to make regulatory
decisions about the human health and environmental effects of these
pesticide products. EPA is also proposing to update the definitions of
a biochemical pesticide and a microbial pesticide to more accurately
describe these categories of pesticides, and to make a conforming
change to the definition of microbial pesticide. EPA is announcing its
policy to provide assistance to applicants when needed in determining
what data are appropriate to support registration of a biochemical or
microbial pesticide and encouraging applicants to request pre-
submission meetings to discuss these data issues. EPA is announcing its
intent to provide assistance to applicants in some narrow circumstances
in preparation of an applicant's data waiver.
DATES: Comments must be received on or before June 6, 2006.
ADDRESSES: Submit your comments, identified by docket identification
(ID) number EPA-HQ-OPP-2004-0415, by one of the following methods:
Federal eRulemaking Portal:https://www.regulations.gov. Follow the
on-line instructions for submitting comments.
Mail: Public Information and Records Integrity Branch (PIRIB)
(7502C), Office of Pesticide Programs (OPP), Environmental Protection
Agency, 1200 Pennsylvania Ave., NW., Washington, DC 20460-0001. In
addition, please mail a copy of your comments on the information
collection provisions to the Office of Information and Regulatory
Affairs, Office of Management and Budget (OMB), Attn: Desk Officer for
EPA, 725 17th St. NW., Washington, DC 20503.
Hand Delivery: Public Information and Records Integrity Branch
(PIRIB), Office of Pesticide Programs (OPP), Environmental Protection
Agency, Rm. 119, Crystal Mall 2, 1801 S. Bell St., Arlington,
VA. Such deliveries are only accepted during the Docket's normal hours
of operation, and special arrangements should be made for deliveries of
boxed information.
Instructions: Direct your comments to Docket ID No. EPA-HQ-OPP-
2006-0415. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
https://www.regulations.gov/, including any 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 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 public docket and made available on
the Internet. If you submit an electronic comment, EPA recommends that
you include your name and other contact information in the body of your
comment and with any disk or CD-ROM you submit. If EPA cannot read your
comment due to technical difficulties and cannot contact you for
clarification, EPA may not be able to consider your comment. Electronic
files should avoid the use of special characters, any form of
encryption, and be free of any defects or viruses. For additional
information about EPA's public docket visit the EPA Docket Center
homepage athttps://www.epa.gov/epahome/dockets.htm.
Docket: All documents in the docket are listed in the
regulations.gov index. Although listed in the index, some information
is not publicly available, e.g., CBI or other information whose
disclosure is restricted by statute. Certain other material, such as
copyrighted material, will be publicly available only in hard copy.
Publicly available docket materials are available either electronically
in https://www.regulations.gov or in hard copy at the Public Information
and Records Integrity Branch (PIRIB) (7502C), Office of Pesticide
Programs (OPP), Environmental Protection Agency, Rm. 119, Crystal Mall
2, 1801 S. Bell St., Arlington, VA. This Docket Facility is
open 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: Candace Brassard or Nathanael Martin,
U.S. Environmental Protection Agency (7506C), 1200 Pennsylvania Ave.
NW., Washington, DC 20460, telephone: 703-305-6598 or 703-305-6475, e-
mail: brassard.candace@epa.gov or martin.nathanael@epa.gov. Do not e-
mail your comments to these contacts. Submit your comments according to
the instructions under ADDRESSES.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this Action Apply to Me?
You may be affected by this notice if you are a producer or
registrant of a biochemical or microbial pesticide product. This
proposal also may affect any person or company who might petition the
Agency for new tolerances for biochemical or microbial pesticides, or
hold a pesticide registration with existing tolerances, or any person
or company who is interested in obtaining or retaining a tolerance in
the absence of a registration, that is, an import tolerance for
biochemical or microbial pesticides. The following is intended as a
guide to entities likely to be regulated by this action. The North
American Industrial Classification System (NAICS) codes are provided to
assist you in determining whether or not this action applies to you.
Potentially affected entities may include, but are not limited to:
Chemical Producers (NAICS 32532), e.g., pesticide
manufacturers or formulators of pesticide products, importers or any
person or company who seeks to register a pesticide or to obtain a
tolerance for a pesticide.
Crop Production (NAICS 111).
Animal Production (NAICS 112).
Food Manufacturing and Processing (NAICS 311).
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 could also be affected. If
you have questions regarding the applicability of this action to a
particular entity, please consult the appropriate Branch Chief in the
U.S. EPA Biopesticides and Pollution Prevention Division of the Office
of Pesticide Programs at 703-308-8712, fax number at 703-308-7026 or
visit the following website: https://www.epa.gov/pesticides/
biopesticides/.
[[Page 12073]]
B. What Should I Consider as I Prepare My Comments for EPA?
1. Submitting CBI. Do not submit this information to EPA through
www.regulations.gov or e-mail. Clearly mark the part or all of the
information that you claim to be CBI. For CBI information in a disk or
CD ROM that you mail to EPA, mark the outside of the disk or CD ROM as
CBI and then identify electronically within the disk or CD ROM the
specific information that is claimed as CBI). In addition to one
complete version of the comment that includes information claimed as
CBI, a copy of the comment that does not contain the information
claimed as CBI must be submitted for inclusion in the public docket.
Information so marked will not be disclosed except in accordance with
procedures set forth in 40 CFR part 2.
2. Tips for preparing your comments. When submitting comments,
remember to:
i. Identify the document by docket 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. Overview of EPA's Proposal
EPA is proposing to update and revise its data requirements for the
registration of microbial and biochemical pesticide products to reflect
current scientific knowledge. These proposed revisions are intended to
provide EPA with data and other information necessary to support the
registration of a biochemical and microbial pesticide product, and will
improve the Agency's ability to make regulatory decisions about the
human health and environmental effects of these pesticide products.
Since the data requirements were first codified in 1984,
information needed to support the registration of a biochemical and
microbial pesticide has evolved as the general scientific understanding
of the potential hazards posed by pesticides has grown. Since 1984, EPA
has developed new and revised data requirements with public
participation, extensive involvement by the scientific community, and
review by the Scientific Advisory Panel (SAP) under Federal
Insecticide, Fungicide, and Rodenticide Act (FIFRA), which have been
imposed on a case-by-case basis. By codifying these data requirements,
the pesticide industry, along with other partners in the regulated
community, will have a better understanding of and could better prepare
for the registration process for biochemical and microbial pesticides.
In addition, the Agency is proposing certain new data requirements in
response to the need for strengthened risk assessment mandated by the
Food Quality Protection Act (FQPA) and FIFRA.
EPA is also proposing to update the definitions of a biochemical
pesticide and a microbial pesticide to more accurately describe these
categories of pesticides, and to make a conforming change to the
definition of microbial pesticide in 40 CFR part 172. EPA is announcing
its policy to provide assistance to applicants when needed in
determining what data are appropriate to support registration of a
biochemical or microbial pesticide and encouraging applicants to
request pre-submission meetings to discuss these data issues. EPA is
announcing its intent to provide assistance to applicants in some
narrow circumstances in preparation of an applicant's data waiver.
This proposed rule is one in a series of proposals to update and
clarify pesticide data requirements. EPA proposed data requirements for
conventional pesticides (70 FR 12276, March 11, 2005) and is developing
data requirements specific to antimicrobial pesticides. In the future,
EPA expects to develop data requirements for plant-incorporated
protectants.
III. Statutory Authorities and Regulatory Framework
EPA is authorized to regulate pesticides under two Federal
statutes. FIFRA regulates the sale, distribution, and use of pesticide
products through a licensing (registration) scheme. The Federal Food,
Drug, and Cosmetic Act (FFDCA), among other things, regulates the
safety of pesticide residues in food and feed. Both FIFRA and FFDCA
were amended in 1996 by the FQPA to strengthen the protections offered,
with particular emphasis on protection of children.
This action is issued under the authority of sections 3, 4, 5, 12,
and 25 of FIFRA (7 U.S.C. 136-136y) and section 408 of FFDCA (21 U.S.C.
346a). The data required for a registration, reregistration,
experimental use permit, or tolerance are listed in 40 CFR part 158.
A. FIFRA
In general, under FIFRA, every pesticide product must be registered
(or specifically exempted from registration under FIFRA section 25(b))
with EPA before it may be sold or distributed in the United States. To
obtain a registration, an applicant or registrant must demonstrate to
the Agency's satisfaction that, among other things, the pesticide
product, when used in accordance with widespread and commonly
recognized practice, will not cause ``unreasonable adverse effects'' to
humans or the environment. This determination, as defined in the
statute, requires the Agency to consider the risks and benefits
associated with the use of a pesticide. EPA must determine that the
safety standard contained in FIFRA is met before granting a Federal
pesticide registration.
1. Registration. Section 3 of FIFRA contains the requirements for
registration. Specifically, FIFRA sec. 3(c)(2) provides EPA broad
authority, before and after registration, to require scientific testing
and submission of the resulting data to the Agency by registrants and
applicants of pesticide products. An applicant for registration must
furnish EPA with substantial amounts of data on the pesticide, its
composition, toxicity, potential human exposure, environmental fate
properties, ecological effects, as well as information on its efficacy
in certain cases. Although the data requirements are imposed primarily
as a part of initial registration, EPA is authorized under FIFRA sec.
3(c)(2)(B) to require a registrant to develop and submit additional
data to maintain a registration. Thispost-registration data call-in
authority recognizes that the scientific underpinnings of risk
assessment change, and is another means by which EPA may keep data for
use in risk assessment current with the evolving science.
2. Reregistration. FIFRA sec. 4 requires that EPA reregister each
pesticide product first registered before November 1984. This date was
chosen based upon the fact that pesticides registered since 1984 were
subject to the 40 CFR part 158 requirements of the 1984 regulations.
Additional data for
[[Page 12074]]
older pesticides were called in where gaps in the scientific data base
occurred. The Agency has used its data call-in authority to require on
a case-by-case basis the submission of most of the data requirements
contained in this proposal.
3. Experimental use permits. Subject to some exemptions, FIFRA sec.
5 requires persons seeking experimental use of pesticides under field
conditions to obtain an experimental use permit (EUP). An EUP allows
limited distribution and use of a pesticide for specified experimental
and data collection purposes intended to support future registration of
the pesticide. Because an EUP is for limited use under controlled
conditions, the data needed to support issuance of the permit are
correspondingly less than those required for full registration. For
example, when performing crop field trials, a registrant may opt to
destroy the treated crop rather than generate the needed residue
chemistry data to establish a temporary tolerance. The regulations
governing the issuance of EUPs are found in 40 CFR part 172.
B. FFDCA
FFDCA mandates EPA to determine that the level of pesticide
chemical residues in food and feed will be safe for human consumption.
An applicant must petition the Agency for a tolerance (maximum residue
level) for a pesticide that is to be used in or around food or feed
commodities, or could otherwise come in contact with food or feed. The
safety standard set under FFDCA sec. 408(b) and (c) defines safe as ``a
reasonable certainty that no harm'' will result from exposures to
pesticide chemical residues. In making this determination, EPA is
directed to assess multiple sources of pesticide exposure, including
anticipated food, drinking water, and other non-occupational exposures
for which there is reliable information. Under FFDCA sec. 408(b)(2)(C),
EPA must make a separate finding of safety for infants and children. In
addition, EPA must take into account a variety of other factors,
enumerated in sec. 408(b)(2)(D), including the cumulative risks
associated with pesticides having a common mechanism of toxicity. The
combination of aggregate exposure and cumulative risk increases the
nature and scope of EPA's risk assessment, and potentially the types
and amounts of data needed to determine that the FFDCA safety standard
is met.
1. Establishing tolerances. Under FFDCA sec. 408, EPA is authorized
to establish tolerances for pesticide residues in food and feed, or to
exempt a pesticide from the requirement of a tolerance, if warranted.
As previously mentioned, in 1996, the FQPA modified the FFDCA to
establish a single health-based standard for tolerance-setting and
enhanced the risk assessment process to more clearly focus on pesticide
risks to children. (In this preamble, references to tolerances include
exemptions from tolerance since the standards and procedures for both
are essentially the same.) The new safety standard applies to
tolerances in a number of regulatory situations, including:
Permanent tolerances that support registration under
FIFRA;
Tolerances for imported products are established to allow
importation of pesticide-treated commodities, but for which no U.S.
registration is sought;
Time-limited tolerances which are established for FIFRA
sec. 18 emergency exemptions; and
Temporary tolerances established for experimental use
permits under FIFRA sec. 5.
2. Reassessing tolerances. Under FFDCA sec. 408(q), EPA must
reassess each tolerance established before August 3, 1996, on a
prescheduled 10-year schedule. The Agency has reassessed many
tolerances under its reregistration program. Numerous regulatory
decisions have been made based upon available data and information
required by the existing data requirements, and supplemented by
additional data provided by registrants through data call-ins or
voluntary submissions.
C. Linking FIFRA and FFDCA Safety Standards
Unless EPA is able to establish or maintain a needed tolerance or
exemption under FFDCA, a pesticide cannot be registered under FIFRA for
a food/feed use. FQPA created a specific linkage (FIFRA sec. 2(bb))
between the ``unreasonable adverse effects'' finding under FIFRA and
the determination of pesticide residue safety of ``reasonable certainty
of no harm'' under FFDCA. In essence, a pesticide that is inconsistent
with, or does not meet, the FFDCA sec. 408 safety standard poses an
unreasonable adverse effect that precludes new or continued
registration. Thus, both FIFRA and FFDCA standards must be met for
pesticides to be registered in the United States for food or feed uses.
Given this linkage between registration and tolerances, it makes
sense for EPA to define data requirements for both purposes: the data
required to support a determination of ``reasonable certainty of no
harm'' under FFDCA are an integral part of the data needed for an
``unreasonable adverse effects'' determination under FIFRA.
Consequently, when promulgated, these proposed data requirements will
encompass the basic data requirements for both registration and
tolerance-setting determinations. EPA will retain its authority to
require additional data on a case-by-case basis.
IV. Background
A. What is the Context for Today's Proposal?
Under FIFRA, as previously stated, every pesticide product must be
registered (or specifically exempted from registration under FIFRA
section 25(b)) with EPA before it may be sold or distributed in the
United States. To obtain a registration, an applicant or registrant
must demonstrate to the Agency's satisfaction that, among other things,
the pesticide product, when used in accordance with widespread and
commonly recognized practice, will not cause ``unreasonable adverse
effects'' to humans or the environment. This safety determination, as
defined in the statute, requires the Agency to consider the risk of the
use of the pesticide and weigh this against its benefit. EPA must
determine that the safety standard contained in FIFRA is met before
granting a Federal registration. The establishment of tolerances, if
appropriate, is part of the registration process.
B. Why does EPA Require Data for Pesticide Registrations?
Under the FFDCA and the FIFRA, anyone seeking to register a
pesticide product is required to provide information to EPA that
demonstrates the product can be used without posing unreasonable risk
to human health and the environment, and for food uses, that there is a
reasonable certainty that no harm will result from exposures to the
residues of the pesticide product. As appropriate for the particular
pesticide product, EPA uses the information provided to evaluate the
pesticide for a wide range of adverse human health effects, from eye
and skin irritation to cancer and birth defects, and to assess how the
pesticide affects animal and plant species, nontarget insect species
and to determine what happens to the pesticide in soil, water, and air.
C. What are the Data Requirements?
First promulgated in 1984, the data requirements in 40 CFR part 158
(49 FR 42856, October 24, 1984) outline the kinds of data and related
information typically needed to register a pesticide. The data
requirements are organized by major pesticide type (e.g., conventional,
[[Page 12075]]
biochemical, microbial, etc.), scientific discipline (e.g.,
toxicology, etc.), and major use sites (e.g., outdoor vs. indoor,
terrestrial, aquatic, greenhouse). Part 158 also outlines the
associated procedures for submitting the data, requesting a waiver from
a requirement(s), and other associated procedures. Since there is much
variety in pesticide chemistry, exposure, and hazard, part 158 is
designed to be flexible. Table notes (referred to as test notes) to
each data requirement explain under what conditions data are typically
needed. The Agency also recognizes, however, that due to the particular
nature and risk of some pesticides, registrants may seek to obtain data
waivers or may suggest alternative approaches to satisfying
requirements.
In essence, the data requirements identify the questions that the
registrant will need to answer regarding the safety of a pesticide
product before the Agency can register it. Data requirements address
both components of a risk assessment, i.e., what hazards do the
pesticide present, and estimated level of exposure to humans or
nontarget species. The answer to one question may inform the kind of
information needed in others. For example, a pesticide that is
persistent and toxicologically potent may require more extensive
exposure data to help establish a safe level of exposure. If there is
negligible exposure then extensive hazard data may not be required
since any conceivable risk would be low.
1. The establishment of standardized data requirements. Until 1984,
data requirements were based on longstanding requirements initially put
in place when pesticides were regulated by the U.S. Department of
Agriculture (USDA) and the Food and Drug Administration (FDA). However,
because virtually all EPA decisions relating to the registration of
pesticides or the establishment of tolerances depend on Agency
evaluation of scientific studies, EPA has throughout the years
developed standardized data requirements and test guidelines, and
established evaluation procedures and peer review processes to ensure
the quality and consistency of scientific studies.
The current provisions in part 158 were originally promulgated in
October 1984. Prior to this, data requirements for the registration of
pesticides were contained in a variety of guidance documents, not in
regulatory form. Part 158 was intended to be a concise presentation of
what data were required and under what circumstances. Once codified,
part 158 specified standard hazard and exposure studies required for
registration and tolerance setting and also identified conditions under
which more specialized studies might be required. Guidelines, i.e.,
instructions and test methods on how to perform a study, had meanwhile
been issued as a series of Pesticide Assessment Guidelines. These
documents, updated in 1996, describe acceptable protocols, test
conditions, and data reporting guidelines to ensure that EPA's
regulatory decisions are based on sound scientific data.
2. Relationship between the harmonized test guidelines and part 158
requirements. EPA has established a unified library for test guidelines
issued by the Office of Prevention, Pesticides, and Toxic Substances
(OPPTS) for use in testing chemical substances to develop data for
submission to EPA under the Toxic Substances Control Act (TSCA), FFDCA,
or FIFRA. This unified library of test guidelines represents an Agency
effort that began in 1991 to harmonize the test guidelines within
OPPTS, as well as to harmonize the OPPTS test guidelines with those of
the Organization for Economic Cooperation and Development (OECD), which
includes representation of countries throughout the world (including
the United States). The process for developing and amending the test
guidelines included several opportunities for public participation and
the extensive involvement of the scientific community, including peer
review by the FIFRA SAP and the Science Advisory Board (SAB) and other
expert scientific organizations.
The purpose for harmonizing these guidelines into a single set of
OPPTS guidelines is to minimize variations among the testing procedures
that must be performed to meet the Agency's data requirements under
FIFRA and TSCA. The guidelines themselves do not impose mandatory
requirements. Instead, they provide recognized standards for conducting
acceptable tests, guidance on reporting data, definition of terms,
consistent with the purpose of the data requirement and the test
standard and recommended study protocols. As such, pesticide
registrants may also use a nonguideline protocol to generate the data
required by part 158. Typically the registrant will use the available
guideline, in which case the study protocol would simply cite the
relevant guideline. If the registrant deviates from these guidelines,
or is asked to provide data where there isn't yet a final guideline
available, the registrant is expected to fully justify the methods
chosen in the study protocol. Nonguideline protocols may be accepted,
provided that the study protocol meets the purpose of the data
requirement and provides data of suitable quality and completeness as
typified by the protocols cited in the guidelines. More information
about the unified library and these guidelines is available a https://
www.epa.gov/opptsfrs/home/guidelin.htm. Please see the docket for the
complete crosswalk for old guideline numbers to new guideline numbers
(Ref. 2).
D. Why have EPA's Data Needs Changed Since 1984?
1. 1988 FIFRA amendments. In 1988, FIFRA was amended to ensure that
older pesticides met the scientific standards of the day. Among other
things, the amendments provided for the acceleration of the
reregistration program by establishing statutory deadlines and new
procedures. During the registration process, EPA recognized that some
of the 1984 data requirements were becoming out of date. The Agency
then called in additional information in order to complete the
registration process.
2. The National Academy of Sciences 1993 Report. With increasing
emphasis on protecting children's health, EPA began to examine its data
requirements relative to evaluating the potential risks from pesticides
to sensitive subpopulations. The Agency sought the advice of the
National Academy of Sciences' National Research Council (NRC) to assess
its risk assessment methodologies and to provide additional information
on the extent to which children may be at risk given emerging
scientific information and technologies. In their 1993 report entitled,
``Pesticides in the Diets of Infants and Children,'' NRC offered
recommendations for further protecting infants and children from
pesticides in their diet. The NRC called for the Agency to require more
data and adopt better risk assessment methodologies. For example, the
Council called for increased testing in the area of immune function and
reproductive testing (National Research Council, 1993, pp. 152-156)
(Ref. 3), which applies to biochemical and microbial pesticides. NRC
also suggested adding a thyroid screen to existing subchronic and
chronic toxicity tests and additional tests of age-related
physiological changes and pharmacokinetics in immature animals. At the
time the 1993 report was released, EPA had already begun work on many
of the recommendations to improve the quality of its risk assessments.
New testing guidelines and protocols were developed. Since then, many
of the
[[Page 12076]]
testing requirements recommended by the NRC have been incorporated into
the Agency's standard evaluation requirements and practices.
3. Scientific Advisory Panel Review of 1994. The FIFRA SAP
completed a review of a set of scientific issues regarding the
Environmental Protection Agency's Proposed Rule: Pesticide Registration
Data Requirements, 40 CFR part 158 (Ref. 4). The Panel commended the
Agency for presenting this regulation in such a clear and
understandable manner, and generally endorsed the revisions. The Panel
addressed individual scientific issues where necessary for both
biochemicals and microbial pesticides and the data needed to address
risk.
4. The Food Quality Protection Act of 1996 (FQPA). Passage of FQPA
in 1996 reformed the nation's pesticide and food safety laws, resulting
in changes in EPA's approach to protecting human health from risks
associated with pesticide use. As mentioned, FQPA modified both FIFRA
and FFDCA and established a single health-based standard for food-use
pesticides and added protections for infants and children. Since the
early 1990s, EPA has been continually working on improving data
requirements. Under FFDCA, as amended by FQPA, EPA must reassess all
existing pesticide tolerances and exemptions against the expanded and
more rigorous safety standard. Beginning in 1994, and increasingly
since the enactment of FQPA, EPA has changed aspects of its data
requirements and risk assessment process to improve its ability to
assess exposure more accurately and to strengthen its understanding of
the potential pesticide risk to children. As mentioned, risk
assessments must now consider data relating to aggregate exposure
(exposure to pesticides from food, drinking water, and nonoccupational
routes such as home and garden uses) and cumulative risk (effects from
exposures to multiple pesticides that share a common mechanism of
toxicity). These measures necessitate collection of additional data on
drinking water and nonoccupational and residential exposure.
5. Pesticide reregistration. Recognizing that pesticides registered
in the past may not meet today's safety standards, EPA is reviewing and
reregistering older pesticides and taking action to reduce risks where
appropriate. On July 13, 2005, EPA published a notice of proposed
rulemaking (NPRM) to establish procedural regulations for conducting
registration review (70 FR 40251, July 13, 2005), as required in FIFRA
section 3(g). Registration review will replace EPA's one-time pesticide
reregistration and tolerance reassessment programs starting in 2006.
The Agency will conduct a review of each pesticide at least every 15
years to ensure that registrations continue to meet statutory standards
for registration. EPA plans to make decisions on almost 50 registration
review cases, or about 80 active ingredients, each year. Under the
reregistration process required by FIFRA section 4, EPA has been
reviewing older pesticides (those initially registered before November
1, 1984) to consider their health and environmental effects and to make
decisions about their future use. EPA is committed to completing the
reregistration process by the end of fiscal 2008.
V. Scope, Purpose, and Request for Comments on this Proposal
A. General Background on the Phased Rulemaking Approach
EPA is responsible for registration of the following categories of
pesticides: Biochemicals, microbials and plant-incorporated
protectants, conventional pesticides, and antimicrobial pesticides. The
various processes include differing data requirements that registrants
must take into account in their submittals.
On March 11, 2005, EPA published a proposed rule to update and
revise its data requirements for the registration of conventional
pesticides (70 FR 12276) (Ref. 5). In addition to proposing specific
changes to the data requirements for registration of conventional
pesticides, EPA proposed a number of other changes to the general
provisions of part 158. Specifically, subpart A of the proposed rule
for conventional chemicals describes general provisions including
definitions, format of data submissions, policies on Confidential
Business Information (CBI), flagging criteria, waivers, and minor uses.
Subpart B of the proposed rule for conventional chemicals describes
expanded use patterns, clarifications on using the data tables,
identifying data for Experimental Use Permits (EUPs), test guidelines,
and purpose of the registration data requirements. That proposed rule
also proposed to upgrade the structure of part 158, assigning
biochemical data requirements to subpart L, and microbial pesticide
data requirements to subpart M of part 158.
Today's proposed rule proposes to update and revise the data
requirements for the registration of biochemical and microbial
pesticides, and to maintain the structure proposed in the earlier
proposed rule for conventional pesticides, by placing the proposed data
requirements for biochemical and microbials in new subparts L and M,
respectively. When the proposed rule for conventional pesticides is
finalized, the general provisions of subparts A and B of that rule will
apply to the other data specific subparts, such as subparts L and M as
proposed today, unless otherwise specified. Future rulemakings will
address the data requirements for antimicrobials and plant-incorporated
protectants.
B. Summary of this Proposal
EPA is proposing a number of changes to the current data tables.
The proposed rule would:
1. Codify current data requirements that do not appear in part 158,
but which are routinely required.
2. Add new data requirements.
3. Revise certain existing data requirements, such as by updating
test notes.
4. Clarify the definitions of both ``biochemical pesticide'' and
``microbial pesticide'' to reflect our current application of those
terms, and make a conforming change in the part 172 definition of
``microbial pesticide.''
5. Add additional definitions needed to apply the data requirements
properly.
6. Make necessary reorganizing and formatting revisions, such as
renaming data requirements.
EPA will retain its current tiering system for both biochemical and
microbial pesticide data requirements.
C. What are the Purposes of this Proposal?
EPA has a number of objectives in proposing this regulation to
update and revise the data requirements in 40 CFR part 158.
1. Ensuring high quality data to meet EPA's mandates. Although most
of the specific requirements in part 158 have not changed since the
data requirements were first published in 1984, aspects of the
requirements may be out of date or may be unclear because the
underlying science has advanced (e.g., National Academy of Sciences
(NAS) in 1993 suggested changes to better protect children) or the
Agency's legislative mandate has been broadened to address new
concerns. For example, given the stricter mandates imposed by the 1988
FIFRA amendments and the 1996 FQPA amendments to FIFRA and FFDCA
(emphasis on exposure to population subgroups), EPA finds that it is
more frequently requesting certain data, and the Agency believes it
should detail more specifically the conditions under which these tests
will be required.
In light of this background, the primary purpose of this proposal
is to
[[Page 12077]]
transparently identify the data EPA needs and will require to support a
determination of ``reasonable certainty of no harm'' under FFDCA and
``unreasonable adverse effects'' determination under FIFRA. In
developing this proposed rule, EPA has evaluated its data needs to
conduct the expanded risk assessments required by new statutory
mandates. Thus, the proposed changes entail both new tests and
broadened requirements for some current tests, reflecting the changes
in data requirement practices that have evolved since the 1984 data
requirement rule was promulgated and addressing data needed to meet
requirements created by statutory amendments to FIFRA and FFDCA.
2. Ensuring a sound scientific basis that is consistent with
advances in scientific understanding and works toward harmonization to
avoid duplicative data. Relatedly, these proposed revisions are
intended to ensure that the data requirements in part 158 reflect
current scientific understanding and scientific advances since the data
requirements were first issued in 1984. As discussed throughout this
document, these proposed revisions have been presented to, and reflect
the advice and recommendations of, the NAS and FIFRA SAP. Issues and
related materials that are brought by EPA to the FIFRA SAP undergo a
public review and comment opportunity before the FIFRA SAP issues its
report with recommendations to the Agency.
To the extent feasible, the proposed revisions are a reflection of
the scientific advances within OECD countries. The United States
participates in OECD activities to harmonize international testing
standards and, where appropriate, reference to the OECD testing
standards have been included in this proposal. However, since EPA
continues to allow applicants to submit and use their own study
protocols consistent with the purpose of the requirement to generate
data that they subsequently submit to EPA, and there are differences in
the mandate and authorities between EPA and the governing authorities
within OECD countries, the data submitted to EPA under part 158 would
be expected to satisfy OECD testing standards under most circumstances
for microbial testing (because OECD has agreed to use the U.S.
microbial pesticide testing guidelines) and for a number of countries
some of the U.S. biochemical testing guidelines would be satisfied. A
few of the governing authorities within the OECD countries may want
additional studies that would not normally be required in the United
States, but protocols for these studies are generally acceptable to all
countries.
3. Improving the depth and transparency of the scientific basis for
pesticide registration decisions. In general, the information developed
as a result of the revisions, if finalized as proposed today, is
expected to improve the depth and transparency of the Agency's
understanding of the health and environmental effects of pesticides to
which individuals and the environment may be exposed. For example, the
proposed rule includes a test note for the human health assessment data
requirements indicating data are not required to support straight chain
lepidopteran pheromones when used at certain application rates. In
addition, EPA is proposing to continue using the tiered testing system,
as given in the current Sec. Sec. 158.690 and 158.740, since many of
the higher tiered data will not be required unless the results from the
lower tiered studies indicate a concern for adverse effects.
4. Improving utility of the part 158 data tables. As described in
the Notice of Proposed Rulemaking on Conventional Pesticides (70 FR
12276, March 11, 2005), EPA has proposed to reorganize and reformat
part 158 subpart A (General Provisions) and subpart B (How to Use Data
Tables), and reorganize and redesignate subpart D (Data Requirement
Tables) into several individual subparts (see Table 1 in Unit VI). In
the proposed reorganization, subpart L is designated for biochemicals
(Sec. 158.900) and subpart M (Sec. 158.1000) is designated for
microbials. Within both subpart L and M, there are definitions,
examples, applicability, and then the series of data requirements in
tables addressing product chemistry, residue chemistry, human health
assessment or toxicology, nontarget organism, and environmental fate.
Many of the revisions proposed in this document are intended to
improve the usefulness of part 158 data tables by better identifying
the specific data requirements that could apply to a particular
pesticide application. As with the original design of part 158 in 1984,
given the variety in pesticide chemistry, exposure, and hazard, these
revisions are intended to retain a fair amount of flexibility in their
application, while improving clarity and transparency to the regulated
community.
5. Reducing burdens where consistent with need for data. In
proposing new and revised data requirements, EPA expects that fewer
data waivers will be needed where the issue is well resolved, e.g.,
straight chain lepidopteran pheromones (SCLPs), and physical chemical
properties criteria outlined in test notes when data are not required.
There are also more transparent test notes indicating when data are
required, while providing assistance to avoid generation of data where
unnecessary. There is also an opportunity to reduce cost of preparation
of waiver requests by providing pre-submission/post-submission meetings
where appropriate.
D. What are Some of the Benefits of this Proposal?
Discussed in more detail in the document entitled ``Economic
Analysis of the Proposed Change in Data Requirements Rule for
Biochemical and Microbial Pesticides,'' which is available in the
docket for this rulemaking (Ref. 6), the following briefly highlights
the benefits anticipated from this proposal:
1. More refined assessments mean clearer understanding of real
risks. EPA's current applicator/user exposure data base is not
comprehensive, especially regarding exposures to pesticides in
nonagricultural settings. The new data that would be collected under
this proposal would allow the Agency to conduct improved exposure
assessments for applicators/users (i.e., especially for insect
repellents). This will benefit growers, other workers, and consumers by
allowing EPA to make better informed regulatory decisions that are
neither too stringent nor too lenient.
2. Clarity and transparency to regulated community means savings.
The enhanced clarity and transparency of the information presented in
part 158, subparts L and M should enhance the ability of industry to
avoid wasted time and effort. Registrants may save time and money by
understanding when studies are needed. This should allow products to
enter the market earlier, thereby registering safer pesticides sooner
and potentially reducing risks as well as increasing profits. The
addition of some data requirements is likely to further communicate to
domestic and world-wide marketplaces that pesticide products and items
treated with them are safer, thus enhancing the reputation of American
agricultural and nonagricultural products and registered pesticides as
tools for public health.
3. Enhanced international harmonization means less duplication. EPA
participates with OECD countries in the development of harmonized
international standards and, to the extent possible, we have included
these revisions in our proposal. The OECD Biopesticide Steering Group
has agreed to use U.S. EPA Harmonized Guidelines for the conduct of
microbial pesticide studies and we continue to work
[[Page 12078]]
together to harmonize our approach to evaluating and reviewing these
data. However, because other OECD countries do not use the tiered
approach to the data requirements, but instead decide on the data
needed for registration on a case-by-case basis, there may be
differences in the actual data required for registration for the United
States compared with other OECD countries. We are presently working
with key OECD biopesticide regulatory representatives to develop OECD
guidance for waiving data, which will bring actual data requirements
closer together. OECD has also recognized pheromones, a certain type of
biochemical pesticide, as warranting a separate, unique set of reduced
data requirements similar to the U.S. data requirements.
4. EPA information assists other communities in assessing pesticide
risks. Scientific, environmental, and health communities find pesticide
toxicity information useful to respond to a variety of needs. For
example, medical professionals are concerned about the health of
patients exposed to pesticides; poison control centers make use of and
distribute information on toxicity and treatment associated with
poisoning; and scientists use toxicity information to characterize the
effects of pesticides and to assess risks of pesticide exposure.
Similarly those responsible for protection of nontarget wildlife need
reliable information about pesticides and assurance that pesticides do
not pose an unreasonable threat. The proposed changes will help the
scientific, environmental, and health communities by increasing the
breadth, quality, and reliability of Agency regulatory decisions by
improving their scientific underpinnings.
5. Better informed users means informed risk-reduction choices.
Better regulatory decisions resulting from the proposed changes should
also mean that the label will provide better information on the use of
the pesticide. A pesticide label is the user's direction for using
pesticides safely and effectively. It contains important information
about where to use, or not use, the product, health and safety
information that should be read and understood before using a pesticide
product, and how to dispose of that product. This benefits users by
enhancing their ability to obtain pesticide products appropriate to
their needs, and to use and dispose of products in a manner that is
safe and environmentally sound. Farmers (as well as other applicators/
users) may benefit from label information based on the data submitted
to the extent it helps inform their decisions about whether or how to
use particular pesticides to avoid potential exposure.
E. How will this Proposal Affect Existing Registrations?
This proposal codifies existing practices by requiring
data that are necessary to complete a risk assessment that are not
included in the current data requirements.
This proposal imposes new requirements for future
registrations, as is the case for applicator/user exposure data to
assess impacts from insect repellents.
In rare circumstances, the Agency may find it necessary to
call in data on certain existing registrations, as warranted by
emerging risk issues.
F. Request for Comments
The Agency invites the public to provide its views on the various
options proposed or present any data or information for the Agency to
consider during the development of the final rule. Specifically, the
Agency welcomes specific comments on the following topics of particular
interest to the Agency.
The Agency welcomes specific comments on the need for, value of,
and any alternatives to, the data requirements described in this
document to meet its mandates.
The Agency welcomes comments on the scientific basis of this
proposed rule.
The Agency welcomes specific comments on the clarity of the
proposed data requirements for biochemical and microbial pesticides and
the relationship between the proposed data requirements and EPA's
statutory determinations.
The Agency welcomes specific comments on the transparency of the
proposed definitions, examples, and applicability for both biochemical
and microbial pesticides.
The Agency welcomes comments on its economic analysis of the
proposed rule, as well as on its underlying assumptions, economic data,
and high- and low-cost options and alternatives. Describe any
assumptions and provide any technical information and data used in
preparing your comments. Explain estimates in sufficient detail to
allow for it to be reproduced for validation. As indicated in Unit
V.B.1, EPA's underlying principle in developing the proposed revisions
has been to strike an appropriate balance between the need for adequate
data to make the statutorily mandated determinations and informed risk
management decisions, while minimizing data collection burdens on
biochemical and microbial pesticide applicants.
VI. Background on Regulation of Biochemical and Microbial Pesticides
and Preparation of this Proposed Rule
A. Background of Regulating Biochemical and Microbial Pesticides
The Agency finalized the data requirements to support the
registration of biochemical and microbial pesticides (49 FR 42856,
October 24, 1984) more than 20 years ago. When promulgated in 1984, EPA
distinguished ``biochemical and microbial pesticides'' from
``conventional chemical pesticides'' by ``their unique modes of action,
low use volume, target species specificity or natural occurrence.'' EPA
recognized that biochemical pesticides are inherently different from
conventional pesticides since they are generally naturally-occurring
and have a non-toxic mode of action.
As a result, biochemicals are expected to pose lower potential risk
compared to conventional pesticides. Due to the non-toxic mode of
action and low risk to humans, certain studies are not included in the
Tier I data requirements for biochemical pesticides. This adjustment in
the tiered data requirements was intended to serve as a safety
mechanism. If Tier I testing indicates a toxic mode of action, the
biochemical would be treated as a conventional pesticide, and virtually
the same toxicology and residue data would be required as is required
for a conventional pesticide.
The Agency has confirmed in the past 20 years of regulating
biochemical pesticides that indeed biochemical pesticides can be
classified and regulated with the data requirement tables that have
been designated for biochemical pesticides. The Agency recognizes that
at the time of application for registration there are instances where a
biochemical may not fit the biochemical category and in such cases the
Agency evaluates the pesticide in question as a conventional pesticide.
Ultimately, if a pesticide were to exceed the criteria established for
a biochemical pesticide, the data requirements in the higher tiers
would be required and the process would take longer than if the
application were made as a conventional pesticide, since all data
requirements would not be clearly identified from the onset.
Microbial pesticides are living organisms and, as such, present
much different risk concerns than chemical toxicants. The main concern
for a microbial pesticide is whether it could survive within, and be
pathogenic to, a nontarget species or humans. As a result, required
studies specifically address the potential for these unique
[[Page 12079]]
risks. Some microorganisms do produce toxins. If comparisons of the
microorganisms indicates that taxonomically similar microorganisms have
been reported to be pathogenic, the data set is configured to allow for
use of conventional toxicity testing if needed to evaluate any toxins.
B. History of Development of Biochemical and Microbial Pesticide Data
Requirements and Guidelines
1. Biochemical pesticides history for regulatory activities. The
following provides the history in the regulatory development of the
data requirements for biochemical pesticides since 1984.
1984--Promulgation of 40 CFR part 158 subpart A: Sec.
158.65 Biochemical and Microbial Pesticides and subpart D: Sec.
158.690 Biochemical Pesticide Data Requirements and Microbial Data
Requirements (49 FR 42856, October 24, 1984).
1987--Report of SAP Recommendations: A Set of Issues Being
Considered by the Agency in Connection with Proposed Revision to
Subdivision M, Immunotoxicity Testing of Biochemical Pest Control
Agents (Ref. 7).
1989--Issuance of Subdivision M of the Pesticide Testing
Guidelines Microbial and Biochemical Pest Control Agents (Ref. 8).
Although titled as such, this guideline did not include a discussion on
biochemical guidelines. The Agency still relies on 1982 Pesticide
Assessment Guidelines Subdivision M Biorational Pesticides (Ref. 9) for
the guidelines pertaining to biochemicals (880 series) if there is not
a designated guideline in the conventional pesticide series (i.e., 870
series and 850 series).start here next
1994--Presentation to SAP to discuss data requirements for
all pesticides, including biochemical and microbial pesticides (Ref.
4). Some data requirements were presented to support conventional
pesticides, i.e., applicator/user exposure data to support insect
repellents (Ref. 10).
2. Microbial pesticides history for regulatory activities. The
following provides the history in the regulatory development of the
data requirements for microbials since 1984.
1984--Promulgation of 40 CFR part 158 subpart A: Sec.
158.65 Biochemical and Microbial Pesticides and subpart D: Sec.
158.690 Biochemical Pesticide Data Requirements and Microbial Pesticide
Data Requirements (49 FR 42856, October 24, 1984).
1987--Presentation to SAP in 1987 for microbial pesticides
in preparation for updating the guidelines (Ref. 7) on immunotoxicity
testing.
1989--Issuance of Subdivision M of the Pesticide Testing
Guidelines Microbial and Biochemical Pest Control Agents (Ref. 8). This
was a culmination of the 1987 SAP and public comments.
1994--Presentation to SAP to discuss data requirements for
all pesticides, including biochemical and microbial pesticides (Ref.
4).
This proposed rule proposes to codify the draft data requirements
outlined and presented to the FIFRA SAP in 1994 and in subsequent
meetings. However, EPA is proposing certain revisions for biochemicals
that are also discussed fully in the Agency's proposal for conventional
chemicals (70 FR 12276, March 11, 2005) (Ref. 5). The Agency developed
a complete list of data requirements for biochemicals and microbials
and the year each were presented to FIFRA SAP (Ref. 11). This
reference, the SAP final reports, and relevant documents presented to
the SAP are available in the docket for this proposed rulemaking.
C. EPA Activities in Preparation for this Proposed Rule
1. Consideration of redesigning data requirement tables. While
preparing for this proposed rule, the Agency considered redesigning
data requirements based on subcategories of biochemical and microbial
pesticides. Each subcategory was evaluated based on mode of action and
potential for risk to human health and the environment, with each
subcategory requiring different data to support registration. The
subcategories for biochemical pesticides were as follows: pheromones
(including arthropod, lepidopteran, and straight chain lepidopteran
pheromones), growth regulators (insect and plant), repellents (insect
and others), and other biochemicals (which includes all other
biochemicals). The microbial pesticides includes the following
subcategories: protozoa, viruses, bacteria, and fungi.
In the economic analysis for this proposed rule, the Agency
analyzed the test cost data submitted based on each subcategory to
determine the different data requirements (Ref. 12). Based on the
analysis, the Agency decided it was more appropriate to make the test
notes more clear and transparent, and only update the data requirement
tables without redesigning them based on subcategory.
2. Consistencies between current part 158 and proposed part 158
design of data requirement tables for biochemical and microbial
pesticides. EPA is proposing to continue using the tiered testing
system, as given in the current Sec. 158.690 and Sec. 158.740. For
these specific types of pesticides, it is appropriate to ask for
studies in a tiered scheme because many of the higher tiered data will
not be required unless the results from the lower tiered studies
indicate a concern for adverse effects.
3. Consultations with stakeholders. During the pre-rulemaking
process, the Agency actively sought consultations with industry,
academia, and non-profit organizations (i.e., environmental groups) on
the current regulatory requirements for data and requested input on the
universe of possible changes to the regulatory text. For parties
interested in discussing the development of this rule with EPA,
consultations were held in-person, by telephone conference, and via-
email. During these pre-proposal stage consultations, the Agency did
not request feedback on the changes being proposed today, whether the
proposed changes are newly imposed, newly codified data, or revisions
to existing data requirements. Feedback from these consultations
included the following topics: existing data requirements, industry
burden in fulfilling data requirements, tiered testing approach, and
issuance of guidance specific to test protocols. All the stakeholder
comments are available in the docket (Ref. 13).
D. Consultations with Applicants
In an effort to improve transparency, increase efficiencies and
reduce burdens, EPA is announcing a policy to provide assistance to
applicants when needed in determining what data or information are
appropriate to support registration of a biochemical or microbial
pesticide. EPA is encouraging applicants to request pre-submission
meetings to discuss these data issues. EPA is also announcing its
intent to provide assistance to applicants in some narrow circumstances
in preparation of an applicant's data waiver after submission of an
application.
EPA notes that applications for biochemical and microbial
pesticides frequently involve substances that present low risk (i.e.,
naturally-occurring, non-toxic mode of action, minimal exposure). Data
requirements - even as proposed--may overstate the Agency's need, or
may be satisfied by existing data in the open literature or other
available data or information. In some cases, the applicant may not be
aware of a potential rationale for a waiver or be able to identify
available data or information that may satisfy a data requirement in
lieu of generating new data. Thus, EPA encourages applicants to seek
pre-submission meetings to discuss the appropriate data or information
to support their product
[[Page 12080]]
and the opportunity for requesting data waivers.
1. Pre-submission process. During a pre-submission meeting, EPA may
be aware that certain data requirements are already satisfied by
available data or information. Sources of existing data include public
literature and/or studies submitted by another registrant, which may be
cited with data compensation procedures. EPA may also be aware of sound
scientific rationales that certain data requirements should not be
imposed. For example, the question the required data is intended to
answer might be addressed by a combination of other information or
data, and therefore might be able to be waived. In either case, during
the pre-submission meeting, EPA would discuss with the applicant the
grounds for citing other information or data to conclude that a data
requirement has been met or the grounds for requesting a waiver where
other information or data otherwise addresses the need for a specific
piece of data required by the regulations have been satisfied. The
applicant may then submit an application based on the discussion with
EPA. The application should include a signed copy of the minutes of the
pre-submission meeting listing each data requirement and the reason why
EPA and the company believe a waiver is appropriate. The applicant is
encouraged to submit a copy of the pre-submission meeting minutes to
EPA for concurrence prior to submission of its application for a
waiver.
To some extent, EPA currently offers this assistance to applicants
and is simply encouraging applicants to request pre-submission meetings
and suggesting a process for ensuring consistent reflection of
discussions at the pre-submission meeting.
2. Post-submission process. Even after submission of an application
for registration, EPA may find that either of these scenarios exist
(i.e., basis for citing to other data/information or waiver of a data
requirement). Again, EPA may discuss these issues with the applicant
and the applicant may choose to amend its application by citing to
other data/information or requesting a waiver.
EPA is also announcing its intention to assist applicants in the
actual preparation of a data waiver in some narrow circumstances.
Specifically, in the course of reviewing an application, EPA may find
that in its judgment, data otherwise required by part 158 would not be
necessary to grant the application or are available from other sources.
EPA would notify the applicant and explain the basis for its belief in
writing. If the data are compensable or exclusive in use, the applicant
may submit EPA's letter with the appropriate offer to pay or an
authorization, as an amendment to its application. If the Agency
explains in its correspondence that the data may be waived, the
applicant may use EPA's correspondence to support a waiver request by
signing the correspondence and submitting it as an amendment to its
application. Because the correspondence only includes citation or
discussion of existing data or information, EPA is proposing not to
consider such amendments to an application to be ``data'' subject to
the formatting provisions of Sec. 158.32(a) as proposed on March 11,
2005 (70 FR 12276).
This pre-submission and post-submission process for ensuring that
the data requirements are either satisfied or waived is specific to the
review of biochemical and microbial registration applications, due
primarily to the specific nature and circumstances unique to these
pesticides (e.g., information already known to the Agency) and thus the
Agency does not anticipate this process being widely applicable to
other types of pesticides, such as conventional or antimicrobial
pesticides.
EPA notes that in providing this assistance during the pre-
submission and post-submission process, it will only consider readily
accessible information, such as information found in Agency databases,
and will not search for applicable information, data, or literature.
Further, although intending to help applicants in supporting their
applications, EPA does not encourage applicants to rely on this process
to fill informational data gaps; doing so may be at the expense of
timely review or may ultimately result in rejection of an application
or petition.
Finally, providing assistance in this manner does not effectively
allow app