Pesticides; Policies Concerning Products Containing Nanoscale Materials; Opportunity for Public Comment, 35383-35395 [2011-14943]
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Federal Register / Vol. 76, No. 117 / Friday, June 17, 2011 / Proposed Rules
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regulations at 326 Indiana
Administrative Code (IAC) 2–2–1 and
326 IAC 2–2–4.13
Indiana is currently a SIP-approved
state for the PSD program, and has
incorporated EPA’s 2002 NSR reform
revisions (67 FR 80186) for PSD into its
SIP (72 FR 33395). In a letter provided
to EPA on July 23, 2010, Indiana
notified EPA of its interpretation that
the state currently has the authority to
regulate GHGs under its 326 IAC 2–2
PSD regulations. The current Indiana
program (adopted prior to the
promulgation of EPA’s Tailoring Rule)
applies to major stationary sources
(having the potential to emit at least 100
tpy or 250 tpy or more of a regulated
NSR pollutant, depending on the type of
source) or modifications undertaken in
areas designated attainment or
unclassifiable with respect to the
NAAQS.
Indiana has revised 326 IAC 2–2–1 to
add GHG-related language to the
definitions of ‘‘regulated NSR pollutant’’
and ‘‘significant’’ and to add a new
definition for ‘‘subject to regulation.’’
We find these revisions to be consistent
with the Tailoring Rule.
In 326 IAC 2–2–4, Indiana has added
language that says the air quality
analysis requirements of this section
shall not apply with respect to GHGs.
This does not affect the air qualityrelated requirements elsewhere in the
PSD rule, including requirements for
source information (326 IAC 2–2–10),
additional impact analysis (326 IAC 2–
2–7), or additional requirements for
sources impacting Federal Class I areas
(326 IAC 2–2–14). We find this revision
to be approvable.
V. What action is EPA taking?
EPA is proposing to approve Indiana’s
December 3, 2010, SIP submittal,
relating to PSD requirements for GHGemitting sources in 326 IAC 2–2–1 and
326 IAC 2–2–4. Specifically, Indiana’s
December 3, 2010, proposed SIP
revision establishes appropriate
emissions thresholds for determining
PSD applicability to new and modified
GHG-emitting sources in accordance
with EPA’s Tailoring Rule. EPA has
made the preliminary determination
that this SIP submittal is approvable
because it is in accordance with the
CAA and EPA regulations regarding
PSD permitting for GHGs.
13 Attachment A to the December 3, 2010,
submittal includes revisions to 326 IAC 2–7 to add
GHG provisions to Indiana’s Title V regulations.
However, these regulations are not part of the SIP
and IDEM has not included 326 IAC 2–7 in the
December 3, 2010, request for SIP approval. IDEM
intends to make a separate submittal requesting
approval of the 326 IAC 2–7 regulatory revisions.
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If EPA does approve Indiana’s
changes to its air quality regulations to
incorporate the appropriate thresholds
for GHG permitting applicability into
Indiana’s SIP, then 40 CFR 52.773(k), as
included in EPA’s SIP Narrowing Rule,
which codifies EPA’s limiting its
approval of Indiana’s PSD SIP to not
cover the applicability of PSD to GHGemitting sources below the Tailoring
Rule thresholds, is no longer necessary.
In this proposed action, EPA is also
proposing to amend 40 CFR 52.773 to
remove this unnecessary regulatory
language.
VI. Statutory and Executive Order
Reviews
Under the CAA, the Administrator is
required to approve a SIP submission
that complies with the provisions of the
CAA and applicable Federal regulations.
42 U.S.C. 7410(k); 40 CFR 52.02(a).
Thus, in reviewing SIP submissions,
EPA’s role is to approve state choices,
provided that they meet the criteria of
the CAA. Accordingly, this action
merely approves state law as meeting
Federal requirements and does not
impose additional requirements beyond
those imposed by state law. For that
reason, this action:
• Is not a ‘‘significant regulatory
action’’ subject to review by the Office
of Management and Budget under
Executive Order 12866 (58 FR 51735,
October 4, 1993);
• Does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act (44
U.S.C. 3501 et seq.);
• Is certified as not having a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act
(5 U.S.C. 601 et seq.);
• Does not contain any unfunded
mandate or significantly or uniquely
affect small governments, as described
in the Unfunded Mandates Reform Act
of 1995 (Pub. L. 104–4);
• Does not have Federalism
implications as specified in Executive
Order 13132 (64 FR 43255, August 10,
1999);
• Is not an economically significant
regulatory action based on health or
safety risks subject to Executive Order
13045 (62 FR 19885, April 23, 1997);
• Is not a significant regulatory action
subject to Executive Order 13211 (66 FR
28355, May 22, 2001);
• Is not subject to requirements of
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (15 U.S.C. 272 note) because
application of those requirements would
be inconsistent with the CAA; and
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• Does not provide EPA with the
discretionary authority to address, as
appropriate, disproportionate human
health or environmental effects, using
practicable and legally permissible
methods, under Executive Order 12898
(59 FR 7629, February 16, 1994).
In addition, this rule does not have
Tribal implications as specified by
Executive Order 13175 (65 FR 67249,
November 9, 2000), because the SIP is
not approved to apply in Indian country
located in the state, and EPA notes that
it will not impose substantial direct
costs on Tribal governments or preempt
Tribal law.
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Incorporation by
reference, Intergovernmental relations,
and Reporting and recordkeeping
requirements.
Dated: June 9, 2011.
Susan Hedman,
Regional Administrator, Region 5.
[FR Doc. 2011–15102 Filed 6–16–11; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Chapter I
[EPA–HQ–OPP–2010–0197; FRL–8877–9]
RIN 2070–ZA11
Pesticides; Policies Concerning
Products Containing Nanoscale
Materials; Opportunity for Public
Comment
Environmental Protection
Agency (EPA).
ACTION: Proposed policy statement.
AGENCY:
EPA seeks comment on
several possible approaches for
obtaining information about what
nanoscale materials are present in
registered pesticide products. Under one
approach, EPA would use section 6(a)(2)
of the Federal Insecticide, Fungicide,
and Rodenticide Act (FIFRA) to obtain
information regarding what nanoscale
material is present in a registered
pesticide product and its potential
effects on humans or the environment.
If EPA adopts this approach, 40 CFR
152.50(f)(3) would also require the
inclusion of such information with any
application for registration of a pesticide
product that contains a nanoscale
material. Under an alternative approach,
EPA would obtain such information
using Data Call-In notices (DCIs) under
FIFRA section 3(c)(2)(B). If EPA adopts
this alternate approach, EPA would also
SUMMARY:
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need to require the inclusion of this
information with any application for
registration of a pesticide product that
contains a nanoscale material. It is
EPA’s view that FIFRA section 6(a)(2) is
the most efficient and expedient
administrative approach to obtaining
information about nanoscale materials
in pesticides and EPA would prefer to
use this approach. EPA is also
proposing a new approach for how EPA
will determine on a case-by-case basis
whether a nanoscale active or inert
ingredient is a ‘‘new’’ active or inert
ingredient for purposes of FIFRA and
the Pesticide Registration Improvement
Act (PRIA), even when an identical,
non-nanoscale form of the nanoscale
ingredient is already registered.
DATES: Comments must be received on
or before July 18, 2011.
ADDRESSES: Submit your comments,
identified by docket identification (ID)
number EPA–HQ–OPP–2010–0197, by
one of the following methods:
• Federal eRulemaking Portal: https://
www.regulations.gov. Follow the on-line
instructions for submitting comments.
• Mail: Office of Pesticide Programs
(OPP) Regulatory Public Docket (7502P),
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001.
• Delivery: OPP Regulatory Public
Docket (7502P), Environmental
Protection Agency, Rm. S–4400, One
Potomac Yard (South Bldg.), 2777 S.
Crystal Dr., Arlington, VA. Deliveries
are only accepted during the Docket
Facility’s normal hours of operation
(8:30 a.m. to 4 p.m., Monday through
Friday, excluding legal holidays).
Special arrangements should be made
for deliveries of boxed information. The
Docket Facility telephone number is
(703) 305–5805.
Instructions: Direct your comments to
docket ID number EPA–HQ–OPP–2010–
0197. EPA’s policy is that all comments
received will be included in the docket
without change and may be made
available on-line at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through regulations.gov or email. The regulations.gov Web site is an
‘‘anonymous access’’ system, which
means EPA will not know your identity
or contact information unless you
provide it in the body of your comment.
If you send an e-mail comment directly
to EPA without going through
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regulations.gov, your e-mail address
will be automatically captured and
included as part of the comment that is
placed in the docket and made available
on the Internet. If you submit an
electronic comment, EPA recommends
that you include your name and other
contact information in the body of your
comment and with any disk or CD–ROM
you submit. If EPA cannot read your
comment due to technical difficulties
and cannot contact you for clarification,
EPA may not be able to consider your
comment. Electronic files should avoid
the use of special characters, any form
of encryption, and be free of any defects
or viruses.
Docket: All documents in the docket
are listed in the docket index available
at https://www.regulations.gov. Although
listed in the index, some information is
not publicly available, e.g., CBI or other
information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
is not placed on the Internet and will be
publicly available only in hard copy
form. Publicly available docket
materials are available either in the
electronic docket at https://
www.regulations.gov, or, if only
available in hard copy, at the OPP
Regulatory Public Docket in Rm. S–
4400, One Potomac Yard (South Bldg.),
2777 S. Crystal Dr., Arlington, VA. The
hours of operation of this Docket
Facility are from 8:30 a.m. to 4 p.m.,
Monday through Friday, excluding legal
holidays. The Docket Facility telephone
number is (703) 305–5805.
FOR FURTHER INFORMATION CONTACT: Jed
Costanza, Antimicrobials Division
(7510P), Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001; telephone number:
(703) 347–0204; fax number: (703) 308–
8005; e-mail address:
costanza.jed@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. What is this document about?
This document describes several
possible approaches for obtaining
certain additional information on the
composition of pesticide products. The
notice focuses particularly on
information about what nanoscale
materials are present in registered
pesticide products. In connection with
this document, EPA describes
‘‘nanoscale material’’ as an active or
inert ingredient and any component
parts thereof intentionally produced to
have at least one dimension that
measures between approximately 1 and
100 nanometers (nm).
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Under one approach, EPA would use
section 6(a)(2) of the Federal Insecticide,
Fungicide, and Rodenticide Act (FIFRA)
to obtain information regarding what
nanoscale material is present in a
registered pesticide product and its
potential effects on humans or the
environment. If EPA adopts this
approach, 40 CFR 152.50(f)(3) would
also require the inclusion of such
information with any application for
registration of a pesticide product that
contains a nanoscale material.
Under an alternative approach, EPA
would obtain such information using
Data Call-In notices (DCIs) under FIFRA
section 3(c)(2)(B). If EPA adopts this
alternate approach, EPA would also
need to require the inclusion of this
information with any application for
registration of a pesticide product that
contains a nanoscale material. EPA is
reviewing whether this could be done
under existing regulations or whether
EPA would need to amend existing
regulations to clarify that the
information is required with any
application for registration.
It is EPA’s view that FIFRA section
6(a)(2) is the most efficient and
expedient administrative approach to
obtaining information about nanoscale
materials in pesticides and EPA would
prefer to use this approach.
This document also proposes a new
approach for how EPA will determine
on a case-by-case basis whether a
nanoscale active or inert ingredient is a
‘‘new’’ active or inert ingredient for
purposes of FIFRA and the Pesticide
Registration Improvement Act (PRIA),
even when an identical, non-nanoscale
form of the nanoscale ingredient is
already registered.
After considering any public
comments on the use of FIFRA section
6(a)(2) or DCIs under FIFRA section
3(c)(2)(B), as well as public comments
submitted in response to other questions
posed in this document, EPA plans to
issue a subsequent document in the
Federal Register announcing its
approach to gather this information.
EPA is also asking for specific input on
the proposed approach for determining
whether a nanoscale material is ‘‘new’’
under FIFRA and PRIA.
B. Does this action apply to me?
This action is directed to those
persons who manufacture, distribute,
sell, apply, or regulate pesticide
products, including agricultural,
commercial, and residential products
(NAICS codes 32532 and 32561). 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
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listed in this unit could also be affected.
The North American Industrial
Classification System (NAICS) codes
have been provided to assist you and
others in determining whether this
action might apply to certain entities. If
you have any questions regarding the
applicability of this action to a
particular entity, consult the person
listed under FOR FURTHER INFORMATION
CONTACT.
C. What should I consider as I prepare
my comments for EPA?
1. Submitting CBI. Do not submit this
information to EPA through
regulations.gov or 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 ID
number and other identifying
information (subject heading, Federal
Register date and page number).
ii. Follow directions. The Agency may
ask you to respond to specific questions
or organize comments by referencing a
Code of Federal Regulations (CFR) part
or section number.
iii. Explain why you agree or disagree;
suggest alternatives and substitute
language for your requested changes.
iv. Describe any assumptions and
provide any technical information and/
or data that you used.
v. If you estimate potential costs or
burdens, explain how you arrived at
your estimate in sufficient detail to
allow for it to be reproduced.
vi. Provide specific examples to
illustrate your concerns and suggest
alternatives.
vii. Explain your views as clearly as
possible.
viii. Make sure to submit your
comments by the comment period
deadline identified.
II. Applicable Statutory and Regulatory
Requirements
As a general matter, pesticides may
not be sold or distributed in the United
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States unless they are registered with
EPA. FIFRA section 3(a) (7 U.S.C.
136a(a)). In order to obtain a pesticide
registration, an applicant must provide
EPA with data (or cite existing data)
demonstrating that the proposed
registration complies with the
requirement for registration. FIFRA
section 3(c)(1)(F) (7 U.S.C.
136a(c)(1)(F)). FIFRA contains two
provisions under which EPA may
register pesticides: Section 3(c)(5) for
‘‘unconditional’’ registration and section
3(c)(7) for ‘‘conditional’’ registration (7
U.S.C. 136a(c)(5) and 7 U.S.C.
136a(c)(7)). Importantly, EPA must
make statutorily required findings for
each and every pesticide product for
which registration is sought, regardless
of whether another pesticide product
with the same or similar composition
and use patterns is already registered.
The standard for determining whether
an application should be granted
unconditionally is found in FIFRA
section 3(c)(5). This section provides
that, in order to grant a registration, EPA
must find that a product’s composition
warrants the proposed claims for it; that
the product’s labeling and other
material required to be submitted
comply with FIFRA; that the product
will perform its intended function
without causing unreasonable adverse
effects on the environment; and that,
when used in accordance with
widespread and commonly recognized
practice, the product will not cause
unreasonable adverse effects on the
environment.
FIFRA defines ‘‘unreasonable adverse
effects on the environment’’ as
including ‘‘any unreasonable risk to
man or the environment, taking into
account the economic, social, and
environmental costs and benefits of the
use of any pesticide.’’ FIFRA section
2(bb) (7 U.S.C. 136(bb)). Thus, a critical
aspect of determining whether or not a
pesticide product should be granted a
registration is an evaluation of whether
the benefits associated with the use of
a pesticide outweigh the risks associated
with such use. The burden of
demonstrating that a product meets the
standards for registration rests at all
times on the registrant or applicant for
registration. See, e.g., Industrial Union
Dept. v. American Petroleum Institute,
448 U.S. 607, 653 n. 61 (1980);
Environmental Defense Fund v. EPA,
510 F.2d 1292, 1297, 1302 (DC Cir.
1975).
The Agency has promulgated
regulations in 40 CFR parts 158 and 161
which identify the types of data EPA
expects an applicant to provide to
support an application for registration of
a pesticide product. The Agency
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requires a wide variety of studies in
order to evaluate whether a pesticide
will cause unreasonable adverse effects
on the environment. These required
studies include both toxicity tests and
data to characterize exposure to a
pesticide, including extensive
information on a product’s composition,
and its fate in the environment and
within the human body. For certain
pesticides EPA also requires data on
product efficacy.
If an applicant cannot provide
necessary data for EPA to make the
determinations required to register a
product unconditionally under FIFRA
section 3(c)(5), EPA may still be able to
register the product ‘‘conditionally’’
under FIFRA section 3(c)(7). FIFRA
section 3(c)(7) authorizes EPA to register
a pesticide product on the condition
that the applicant provides additional
data necessary to support a finding that
the product meets the statutory
standards in FIFRA section 3(c)(5).
FIFRA section 3(c)(7) authorizes
conditional registration in three
circumstances. First, the Agency may
conditionally register a product if EPA
determines, among other things, that the
product is identical or substantially
similar to a currently registered
pesticide or differs only in ways that
would not significantly increase the risk
of unreasonable adverse effects on the
environment, and that approving the
registration in the manner proposed
would not significantly increase the risk
of any unreasonable adverse effect on
the environment. FIFRA section
3(c)(7)(A) (7 U.S.C. 136a(c)(7)(A)).
Products approved under this authority
are commonly called ‘‘me-too
registrations.’’ Second, EPA may register
a pesticide for an additional use, if the
applicant provides data to evaluate the
safety of the new use, and use of the
product would not significantly increase
the risk of unreasonable adverse effects
on the environment compared to
products already registered. FIFRA
section 3(c)(7)(B) (7 U.S.C.
136a(c)(7)(B)). These product approvals
are referred to as ‘‘new use’’
registrations. Finally, EPA may
conditionally register a pesticide
product that contains an active
ingredient not present in any currently
registered pesticide product, if the
Administrator determines that:
1. The applicant has provided all data
necessary to evaluate the safety of the
pesticide, with the exception of any data
which are lacking because the applicant has
not had enough time to generate the data
since learning of the requirement;
2. Use of the pesticide during the time
period needed to develop the additional data
will not cause unreasonable adverse effects
on the environment; and
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3. Use of the pesticide is in the public
interest.
FIFRA section 3(c)(7)(C) (7 U.S.C.
136a(c)(7)(C)).
As with applications for
unconditional registrations, applicants
for conditional registration bear the
burden at all times of demonstrating
that the statutory standards are met.
The Agency’s interest in data to
evaluate the risks and benefits of a
pesticide does not necessarily end once
EPA has registered a pesticide product.
Accordingly, other provisions of FIFRA
allow the Agency to require pesticide
registrants to develop and submit
information the Agency believes it
needs in order to maintain the
registration of pesticide products.
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A. DCI
Under FIFRA section 3(c)(2)(B), EPA
may send a DCI notice to a registrant
requiring the registrant to provide
additional data or other information,
which the registrant may need to
generate or compile. Specifically, ‘‘if the
Administrator determines that
additional data are required to maintain
in effect an existing registration of a
pesticide, the Administrator shall notify
all existing registrants of the pesticide to
which the determination relates and
provide a list of such registrants to any
interested person.’’ Failure to respond to
the DCI can serve as the basis for
suspending the registration of the
product, thereby making it unlawful for
the registrant to sell or distribute the
pesticide.
Generally, EPA’s determination that
additional data are needed is
contemplated to occur for one of the
following five reasons:
1. The Re-registration Program.
Section 4 of FIFRA requires EPA to reassess the health and safety data for all
pesticide active ingredients registered
before November 1, 1984, to determine
whether these ‘‘older’’ pesticides meet
the criteria for registration that would be
expected of a pesticide being registered
today for the first time. Section 4 of
FIFRA directs EPA to use section
3(c)(2)(B) authority to obtain the
required data.
2. The Registration Review Program.
Section 3(g) of FIFRA contains
provisions to help achieve the goal of
reviewing each pesticide every 15 years
to assure that the pesticide continues to
pose no risk of unreasonable adverse
effects on human health or the
environment. Section 3(g) instructs EPA
to use the section 3(c)(2)(B) authority to
obtain the required data.
3. Anticipated Residue/Percent Crop
Treated Information. Under section 408
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of the Federal Food, Drug, and Cosmetic
Act (FFDCA), before a pesticide may be
used on food or feed crops, the Agency
must establish a tolerance for the
pesticide residues on that crop or
establish an exemption from the
requirement to have a tolerance. Section
408(b)(2)(E) and (F) of FFDCA authorize
the use of anticipated or actual residue
(AR) data and percent crop treated
(PCT) data to establish, modify,
maintain, or revoke a tolerance for a
pesticide. FFDCA requires that if AR
data are used, data must be reviewed 5
years after a tolerance is initially
established.
4. The Special Review Program. EPA
may conduct a Special Review if EPA
believes that a pesticide poses risks of
unreasonable adverse effects on human
health or the environment. In the
Special Review Program, EPA focuses
on specific hazards or uses of a
pesticide. Special Reviews are not
intended to be comprehensive
evaluations of the pesticide; instead the
Special Review DCIs are to address the
specific hazard or exposure concerns
that are at issue.
5. Enforcement and Unanticipated
Circumstances. The need for a DCI may
arise from the discovery of deficiencies
in previously submitted data, or from
the discovery of specific attributes of the
pesticide or its ingredients. This may
lead the Agency to determine that
additional information is necessary to
reassess whether the pesticide will
cause unreasonable adverse effects on
the environment. This type of DCI is
needed because the concern and
therefore the need for data arise not
from a mandated review program like
Re-registration or Registration Review
described above, but from unanticipated
circumstances. Section 3(c)(2)(B) of
FIFRA provides a means of obtaining
any needed data.
B. FIFRA Section 6(a)(2)
FIFRA section 6(a)(2) provides that
registrants must inform the Agency of
relevant information relating to their
products, even though it was not
specifically requested by EPA.
Specifically, FIFRA section 6(a)(2)
requires that, ‘‘[i]f at any time after the
registration of a pesticide the registrant
has additional factual information
regarding unreasonable adverse effects
on the environment of the pesticide, the
registrant shall submit such information
to the Administrator.’’ (7 U.S.C.
136d(a)(2)). For over 30 years, EPA has
interpreted this provision expansively
to include not only information relating
directly to adverse effects caused by
pesticides, but also to other types of
information and studies that EPA would
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typically use in assessing whether a
pesticide meets the statutory standard
for registration (i.e., the ‘‘unreasonable
adverse effects on the environment’’
risk/benefit standard). See 43 FR 37611
(August 23, 1978).
In 1997, EPA promulgated a final rule
at 40 CFR part 159, subpart D in the
Federal Register issue of September 19,
1997 (62 FR 49370) (FRL–5739–1),
setting forth EPA’s interpretation and
enforcement policy regarding FIFRA
section 6(a)(2). The rule explains,
among other things, what information
EPA regards as ‘‘additional’’ and
‘‘factual,’’ as well as how quickly and to
whom such information must be
reported. The regulation specifies many
kinds of information, from varied
scientific disciplines, that EPA requires
registrants to submit pursuant to FIFRA
section 6(a)(2). The types of information
reflect the variety of scientific data used
by EPA in making the statutorily
required determinations—whether
pesticides cause unreasonable adverse
effects on the environment. Thus, for
example, the regulations generally
require registrants to report studies
indicating that a pesticide causes new or
a higher incidence of toxic effects than
previously identified (see 40 CFR
159.165) and to report incidents
involving injury to humans, pets, or
wildlife resulting from exposure to a
pesticide (40 CFR 159.184). But, EPA
uses other types of information that do
not directly demonstrate adverse effects
in its risk assessments, and new factual
information of this kind is also
reportable under the regulation. For
example, registrants must report studies
that identify new metabolites,
degradates, impurities, or contaminants
of pesticides (40 CFR 159.179); certain
information on the detection of
pesticide residues in water, food, and
feed (40 CFR 159.178); and new studies
of human exposure (40 CFR 159.170). In
sum, EPA’s regulation requires reporting
of many types of information relevant to
EPA’s assessment of the safety of a
pesticide product—in the words of
section 6(a)(2) ‘‘information regarding
unreasonable adverse effects on the
environment of the pesticide’’—not
merely information that directly
concerns adverse effects.
In promulgating that regulation,
however, EPA also recognized it was
impossible to establish rules addressing
every type of factual information that
might become relevant in the future to
judging whether a registered pesticide
product continued to meet the FIFRA
statutory standards. Accordingly, 40
CFR 159.195(a) provides:
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The registrant shall submit to the
Administrator information other than that
described in §§ 159.165 through 159.188 if
the registrant knows, or reasonably should
know, that if the information should prove to
be correct, EPA might regard the information
alone or in conjunction with other
information about the pesticide as raising
concerns about the continued registration of
a product or about the appropriate terms and
conditions of registration of a product.
In addition, 40 CFR 159.195(c) provides
that:
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[t]he registrant shall submit * * *
information other than that described in
§§ 159.165 through 159.188 if the registrant
has been informed by EPA that such
additional information has the potential to
raise questions about the continued
registration of a product or about the
appropriate terms and conditions of
registration of a product.
Thus, once the Agency has informed
registrants that EPA considers a
particular type of information relevant
to determining whether a pesticide has
the potential to cause unreasonable
adverse effects on the environment, that
type of information becomes reportable
under FIFRA section 6(a)(2).
Finally, EPA promulgated a regulation
at 40 CFR part 152 addressing the
submission of applications for
registration (53 FR 15952, May 4, 1988)
(FRL–3266–9b). That rule specifies,
among other things, certain types of
information that an application for
registration of a pesticide product must
contain. The rule provides that the
applicant must ‘‘furnish with his
application any factual information of
which he is aware regarding
unreasonable adverse effects of the
pesticide on man or the environment,
which would be required to be reported
under FIFRA section 6(a)(2), if the
product were registered.’’ 40 CFR
152.50(f)(3).
Registrants’ compliance with FIFRA
section 6(a)(2) and EPA’s implementing
regulations in 40 CFR parts 152 and 159
ensures that EPA has access to any
additional factual information that
could be important for determining
whether a previous Agency decision to
register a pesticide remains a correct
one, and whether a registered pesticide
can in fact be used without posing
unreasonable adverse effects to human
health and the environment. This
provision of FIFRA recognizes that
registrants may come into the
possession of important new
information that was not anticipated by
the Agency or of information the
importance of which was not previously
known, and that in the absence of
registrants submitting such information,
EPA might well remain unaware of the
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information. Failures to report required
information, or delays in reporting, are
regarded by EPA as violations of FIFRA
section 6(a)(2), which in turn makes
them actionable under FIFRA sections
12(a)(2)(B)(ii) and 12(a)(2)(N) (7 U.S.C.
136j(a)(2)(B)(ii) and 7 U.S.C.
136j(a)(2)(N)).
III. EPA’s Interest in Nanoscale
Materials as Pesticide Ingredients
EPA believes that certain information
concerning pesticide ingredients, which
applicants and registrants have not
routinely provided previously, is
relevant to the Agency’s statutory
obligation to determine whether the
registration of a pesticide may cause
unreasonable adverse effects on the
environment. For the reasons discussed
below, EPA is particularly interested in
nanoscale materials in this context.
Accordingly, EPA is considering how to
collect information about what
nanoscale materials are in pesticide
products and is therefore soliciting
public comment on two possible
approaches. It is important to first
clarify how the term ‘‘nanoscale
material’’ is being used for purposes of
this document.
A. Nanoscale Material
To date, EPA has not developed
formal definitions for the terms
‘‘nanotechnology’’ or ‘‘nanoscale
materials’’ or any similar terms for
regulatory purposes under any statute
administered by the Agency. Broad
definitions for the terms
‘‘nanotechnology’’ or ‘‘nanoscale
materials’’ and discussions of
nanotechnology generally reflect the
same common elements, namely:
1. The material’s particle size
measures typically between
approximately 1 and 100 nm in at least
one dimension;
2. The material exhibits unique or
novel properties compared to larger
particles of the same material; and
3. Rather than occurring naturally, the
material has been manufactured or
engineered at the nanoscale to take
advantage of these unique properties.
See, for example, the definition from the
National Nanotechnology Initiative at:
https://www.nano.gov/html/facts/
whatIsNano.html.
These elements do not readily work in
a regulatory context because of the high
degree of subjectivity involved with
interpreting such phrases as ‘‘unique or
novel properties’’ or ‘‘manufactured or
engineered to take advantage of these
properties.’’ Moreover, the contribution
of these subjective elements to risk has
not been established.
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Instead, OPP will focus on more
objective criteria in describing when
information about a ‘‘nanoscale
material’’ in a pesticide product may be
relevant to determining whether the
product has an unreasonable adverse
environmental effect. Specifically, such
information may be relevant in this
context when the active or inert
ingredient and any component parts
thereof is intentionally produced to
have at least one dimension that
measures between approximately 1 and
100 nanometers, regardless of the
aggregation or agglomeration state of the
final material.
In determining whether an ingredient
meets this description, EPA may review
particle size data and, among other
things, the manufacturing process to
determine whether it employs processes
specifically to create or enhance the
proportion of nanoscale materials in the
product, as compared with other
processes used to produce similar
products. The Agency generally expects
that these ingredients may comprise, but
are not limited to, metal-based (e.g.,
silver) and carbon-based (e.g., carbon
nanotubes) nanoscale materials. The
Agency does not, however, intend this
description to cover biological materials
(e.g., DNA, RNA, proteins) or materials
in their natural state (e.g., clays). To the
extent that the application of this
description to a particular product or
ingredient is unclear, EPA would review
information provided by a registrant or
applicant concerning the composition of
the pesticide product and to provide an
Agency view on whether the product
did (or did not) contain a nanoscale
material for purposes of this policy.
B. Potential of Nanoscale Materials To
Affect Human Health and the
Environment
There is a growing body of scientific
evidence showing that differences can
exist between nanoscale material(s) and
their non-nanoscale counterpart(s) (Ref.
1). Nanoscale materials may have
different or enhanced properties—for
example, electrical, chemical, magnetic,
mechanical, thermal, or optical
properties—or features, such as
improved hardness or strength, that are
highly desirable for applications in
commercial, medical, military, and
environmental sectors (Ref. 2). These
properties are a direct consequence of
small size, which results in a larger
surface area per unit of volume and/or
quantum effects that occur at the
nanometer scale (i.e., 1 x 0¥9 meters).
Small size itself is also a desirable
property of nanoscale materials that is
exploited for miniaturization of
applications/processes and/or
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stabilization or delivery of payloads to
diverse environments or incorporation
into diverse products.
Nanoscale materials have a range of
potentially beneficial public and
commercial applications, including
medicine and public health, clean
energy through more efficient solar
panels, pollution reduction and
environmental cleanup, and improved
products such as stronger, lighter, and
more durable or conductive materials.
These benefits arise from the distinctive
properties of nanoscale materials, in
that they are potentially more
interactive or durable than other
chemicals as a result of their size and
composition. EPA sees the emergence of
nanoscale materials as offering potential
benefits for society in many different
fields, including pest control products.
The use of nanoscale materials in
pesticide products and treated articles
may allow for more effective targeting of
pests, use of smaller quantities of a
pesticide, and minimizing the frequency
of spray-applied surface disinfection.
These could contribute to improved
human and environmental safety and
could lower pest control costs. For
example, as a materials preservative,
nanosilver should maintain its efficacy
longer and require smaller quantities
than other silver preservatives due to an
expected gradual and controlled release
of silver as opposed to the rapid release
of for example, silver from a zeolite
structure or the immediate dissolution
of a silver salt. Therefore EPA seeks to
encourage innovative work in
developing nanoscale materials to
realize these benefits.
However, a number of organizations
have considered whether the small size
of nanoscale materials or the unique or
enhanced properties of nanoscale
materials may, under specific
conditions, pose new or increased
hazards to humans and the
environment. Government, academic,
and private sector scientists in multiple
countries are performing research into
the human health effects of diverse
nanoscale materials, resulting in a
substantial and rapidly growing body of
scientific evidence. Recently,
governmental and expert peer review
organizations have reviewed and
summarized this evidence and offered
views about the implications of this
evidence for environmental and human
health and safety.
For instance, in 2009, the National
Institute of Occupational Safety and
Health (NIOSH) issued a report,
‘‘Approaches to Safe Nanotechnology:
Managing the Health and Safety
Concerns Associated with Engineered
Nanomaterials,’’ which summarized the
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available scientific information about
nanoscale materials and identified the
following potential health and safety
properties:
(Ref. 4).
In another recent survey of scientific
research on nanoscale materials, the
authors reported:
• Nanomaterials have the greatest potential
to enter the body through the respiratory
system if they are airborne and in the form
of respirable-sized particles (nanoparticles).
They may also come into contact with the
skin or be ingested.
• Based on results from human and animal
studies, airborne nanoparticles can be
inhaled and deposit in the respiratory tract;
and based on animal studies, nanoparticles
can enter the bloodstream, and translocate to
other organs.
• Experimental studies in rats have shown
that equivalent mass doses of insoluble
incidental nanoparticles are more potent than
large particles of similar composition in
causing pulmonary inflammation and lung
tumors. Results from in vitro cell culture
studies with similar materials are generally
supportive of the biological responses
observed in animals.
• Experimental studies in animals, cell
cultures, and cell-free systems have shown
that changes in the chemical composition,
crystal structure, and size of particles can
influence their oxidant generation properties
and cytotoxicity.
• Studies in workers exposed to aerosols of
some manufactured or incidental
microscopic (fine) and nanoscale (ultrafine)
particles have reported adverse lung effects
including lung function decrements and
obstructive and fibrotic lung diseases. The
implications of these studies to engineered
nanoparticles, which may have different
particle properties, are uncertain.
• Some nanomaterials may initiate
catalytic reactions depending on their
composition and structure that would not
otherwise be anticipated based on their
chemical composition. (Ref. 3).
Many studies have examined the proinflammatory effects of manufactured NPs
[nanoparticles], on the basis that their ability
to cause inflammation is a major predictor of
potential hazard in such particles. The first
important finding was that NPs have a more
pronounced effect on inflammation, cell
damage and cell stimulation than an equal
mass of particles of the same material of
greater size [* * *]. This appears to hold true
for materials as varied as carbon black,
titanium dioxide, various metals and
polystyrene [* * *]. Surface area is the
metric driving the pro-inflammatory effects
and this is evident both in vitro [* * *] and
in vivo [* * *], particles of various sizes
producing inflammatory effects that are
directly related to the surface area dose.
Earlier the same year, the Scientific
Committee on Emerging and Newly
Identified Health Risks (SCENIHR), an
independent scientific committee
advising the European Commission’s
Health and Consumer Directorate,
issued a report, ‘‘Risk assessment of
products of nanotechnologies.’’ The
SCENIHR report identified properties
similar to those identified in the NIOSH
report:
Some specific hazards, discussed in the
context of risk for human health, have been
identified. These include the possibility of
some nanoparticles to induce protein
fibrillation, the possible pathological effects
caused by specific types of carbon nanotubes,
the induction of genotoxicity, and size effects
in terms of biodistribution.
and:
For some nanomaterials, toxic effects on
environmental organisms have been
demonstrated, as well as the potential to
transfer across environmental species,
indicating a potential for bioaccumulation in
species at the end of that part of the food
chain.
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(Ref. 5 [reference numbers in the
original were omitted]).
Other reports in the scientific
literature have indicated that some
nanoscale materials may cross the
placental barrier (Ref. 6) or translocate
to diverse organs following oral
exposure (Ref. 7). Once in these diverse
sites and organs, the large surface area
of nanoscale materials may facilitate
increased reactivity and/or an
inflammatory response, resulting in
toxic effects.
Two recent literature surveys describe
a broad range of effects in nonmammalian species following exposure
to nanoscale materials (Refs. 8 and 9).
These include, for example, increased
ventilation rates, mucus production,
and pathologies, and related alteration
of enzyme activities and indicators of
oxidative stress in rainbow trout,
Oncorhyncus mykiss (Refs. 10 and 11),
and ingestion and accumulation of
nanoscale material in the digestive tract,
as well as mortality, increased heart
rates, and reduced fecundity in Daphnia
magna (Refs. 12, 13, and 14).
Translocation of nano-scale materials
from gill and gut surface to blood and
other organs in exposed Medaka,
Oryzius latipes, has also been reported
(Ref. 15) and carbon nanotubes,
although unable to cross the egg surface,
have been shown to delay hatching in
zebrafish, Danio rerio (Ref. 16). A recent
review of lethal effects and
concentrations determined for a wide
variety of species showed that some
nanoscale materials, including nanotitanium, nano-zinc oxide, nano-silver,
nano-copper oxide, C60, and single- and
multi-walled carbon nanotubes, would
be classified as harmful to extremely
toxic to non-mammalian species (Ref.
17).
While the reports and articles cited
previously have focused primarily on
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differences between nanoscale material
and conventionally sized material of the
same substances, EPA has also
consulted with the FIFRA Scientific
Advisory Panel (SAP) on the extent to
which different types of nanoscale
materials may display different
properties. (The SAP is a Federal
advisory committee consisting of
external, independent, expert, scientific
peer reviewers who provide advice to
EPA on scientific issues involved in the
regulation of pesticides.) In response to
EPA questions on how size and other
properties of nanoscale materials
potentially affect risk and how to assess
such risks, the SAP said: ‘‘Existing data
clearly indicate that many properties of
particles change with size, including
rate of release of ionic forms of metal,
reactivity or catalytic efficiency,
Plasmon resonance, and quantum
effects. * * * The effect of particle size
on biological responses to particle
exposure is less well defined.’’ (Ref. 18).
The SAP also noted that ‘‘[o]ther
physicochemical properties, such as
shape, charge and surface coating, are
also likely to impact biological response
and environmental fate [of nanoscale
materials]. * * * The lack of a clear
understanding of how particle size and
other physical properties affect hazard
profiles led most Panel members to be
unsupportive of bridging among silverbased materials with different
properties.’’ (Ref. 18).
It is important to emphasize that,
while the conclusions described
previously apply to the specific
material(s) and or context in which the
study was conducted, any individual
type of nanoscale material may not
display all or even any of the
characteristics observed and reported
for other nanoscale materials. In other
words, some nanoscale materials may
have properties which, for purposes of
assessing the risk of a pesticide, are
essentially identical to larger sized
materials (or particles) of the same
substance. Furthermore, nanoscale
materials may also have properties that
make them less risky, or more beneficial
in some other way, than larger sized
materials (or particles) of the same
substance. So, it appears increasingly
likely that there are few, if any,
universal ‘‘nanoscale’’ effects, and the
distinctive effects seen at nanoscale are
specific to the properties of each
material type under specific exposure
scenarios. Thus, EPA does not regard
the fact that an ingredient meets our
description of a nanoscale material as
evidence that a pesticide containing the
ingredient would cause unreasonable
adverse effects on the environment and
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thus would no longer meet the statutory
standards for registration. Rather, the
presence of a nanoscale material in a
pesticide is grounds for EPA to consider
the possible need for data to
characterize the potential of the
ingredient to pose risks. However, the
registration status of a product would
not change merely as a result of
providing information to EPA about the
presence of a previously-unreported
nanoscale material. If, based on a
science based assessment of the risks of
the specific pesticide ingredients
involved, EPA were to determine that
the pesticide no longer met the criteria
for registration, or that some change was
needed in the conditions of use, EPA
would conduct a separate action to
notify the manufacturer of that
determination, consistent with current
FIFRA regulations.
Finally, scientifically speaking, there
currently is no bright line with respect
to a size below (or above) which
nanoscale materials do (or do not)
exhibit properties that might be of
interest in assessing whether a pesticide
product has the potential to cause
unreasonable adverse effects on the
environment. Therefore, the precise size
range in nanometers addressed by the
policies proposed in this document
might be revised in the future as new
information becomes available.
C. Nanoscale Materials and Pesticides
The Agency has information
indicating that the use of
nanotechnology has started to expand
into pesticide products, as it already has
in many other fields. For instance, a
number of companies have contacted
EPA expressing an interest in obtaining
registrations for pesticide products
containing ingredients identified as
nanosilver or nanosilver composite
structures (jointly referred to as
‘‘nanosilver’’), and several companies
have submitted applications to register
pesticides containing nanosilver. In
addition, EPA now has information
suggesting that there are other pesticide
products currently registered and in the
marketplace that contain nanosilver as
an active ingredient.
In order for EPA to fulfill its
responsibilities to regulate pesticides
under FIFRA, it needs to determine
whether pesticidal products meet the
statutory standards for registration. As
summarized previously, EPA believes
that what intentionally produced
nanoscale materials are in a pesticide
product, whether as an active or inert
ingredient, is relevant to that
determination. Accordingly, EPA is
considering how to collect information
not only about what nanoscale materials
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are in pesticide products, but also other
information that may be relevant to the
assessment of the potential of such
pesticide products to cause
unreasonable adverse effects on the
environment. Such information may be
important for EPA to determine whether
EPA should continue the registration of
a product, or amend, as appropriate, the
terms and conditions of registration of a
product. EPA is therefore soliciting
public comment on two possible
approaches for obtaining this
information, as discussed in this
document.
IV. Information Relevant To Assessing
the Presence of Nanoscale Materials in
a Pesticide
In light of the foregoing and in
consideration of the potential for
nanoscale material to cause different
effects and to behave differently in the
environment and within organisms from
larger particles of the same substance, as
well as from nanoscale materials with
different characteristics (see Unit III.B.),
EPA believes that any of the following
types of information are relevant to
assessing the potential of a pesticide to
cause unreasonable adverse effects on
the environment:
• Any information concerning what
nanoscale materials are present in
pesticides, whether as an active
ingredient or as an inert ingredient;
• For any pesticide product that
contains nanoscale material, whether
active or inert, any existing information
that characterizes the size and size
distribution of the nanoscale material as
measured in nanometers;
• For any pesticide product that
contains nanoscale materials, whether
active or inert, any existing information
that describes the manufacturing
process used to produce the nanoscale
material in whatever size range it is
produced;
• For any pesticide product that
contains nanoscale materials, whether
active or inert, and that also is or will
be used for an end-use formulation that
contain(s) a composite (e.g., the active
ingredient is a matrix complex
comprised of the nanoscale material(s)
in combination with a carrier, such as
silica or sulfur), any existing
information that characterizes the size
and size distribution of the composite;
and
• For any pesticide product that
contains nanoscale materials, whether
active or inert, any existing information
that shows adverse effects at any level
of exposure to the nanoscale material on
humans or nontarget species, and/or
that shows the levels or nature (e.g.
routes, frequency, or life stage) of
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potential human and environmental
exposure.
Importantly, the foregoing is not
intended to be an exclusive list. To the
extent that a registrant has a pesticide
product that contains a nanoscale
material, and in addition has any other
existing information not captured in the
previous list that pertains to, concerns,
or otherwise relates to the nanoscale
material and has the potential to raise
questions about the continued
registration of a product or the
appropriate terms and conditions of a
product registration, EPA is also
considering whether this too should be
submitted to the Agency.
EPA will review information
submitted concerning what nanoscale
materials are present, including any
existing information not previously
provided to the Agency on size and size
distribution, manufacturing process,
and adverse effects. EPA will use this
and product use information to
determine if it raises any issues, not
previously considered, regarding the
product’s potential to cause
unreasonable adverse effects on the
environment. In some cases, EPA may
determine that additional information is
needed to assess such potential; in this
case, additional data may be required
including data on physical and
chemical properties, rate of nanoscale
material release, and acute, subchronic,
and chronic toxicity to human and
ecological receptors.
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V. Reporting the Presence of Nanoscale
Materials in Pesticide Products
As discussed in Units III. and IV. of
this document, EPA believes that
information about what nanoscale
materials are in pesticide products is
important to its assessment of whether
pesticides meet the statutory standard
for registration. EPA may require such
information under either FIFRA section
6(a)(2) or section 3(c)(2)(B). The Agency
believes that announcing the
applicability of FIFRA section 6(a)(2) to
this type of information would be the
most efficient and expedient
administrative approach to obtaining
existing information about nanoscale
materials in pesticides, in which case
any registrants with this type of
information would be required to report
it to EPA. The Agency is considering,
however, an alternative approach under
which it would issue DCIs under FIFRA
section 3(c)(2)(B) to obtain this
information, in which case registrants
that received the DCI would be required
to respond. This unit of the document
discusses the two possible approaches
and related procedures for obtaining
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information concerning nanoscale
materials in pesticides.
A. FIFRA Section 6(a)(2)
As mentioned previously, FIFRA
section 6(a)(2) and implementing
regulations in 40 CFR part 159 require
pesticide registrants to report certain
information if that information:
1. Is additional;
2. Is factual; and
3. Regards unreasonable adverse
effects on the environment of the
pesticide.
Per 40 CFR 159.195, this includes
information that, if correct, a registrant
knows, or reasonably should know,
would be regarded by EPA, either alone
or in conjunction with other
information about the pesticide, as
raising concerns about the continued
registration of a product or about the
appropriate terms and conditions of
registration of a product.
Announcing the applicability of
FIFRA section 6(a)(2) to information
about nanoscale materials in pesticides
would not mean that EPA is expanding
its interpretation of FIFRA section
6(a)(2) or changing its regulations.
Rather, consistent with EPA’s section
6(a)(2) regulations, EPA would be
merely identifying a set of information
that adds to the subset of reportable
section 6(a)(2) data explicitly identified
at present under the section 6(a)(2)
regulations.
Further, the Agency notes that the
identification of information as
reportable under FIFRA section 6(a)(2)
does not mean that any particular
pesticide or group of pesticides, to
which such information pertains, poses
a risk. Rather, the requirement merely
indicates that EPA has determined that
a particular type of information is
relevant to, and may improve the
Agency’s ability to assess, whether the
pesticide would cause an unreasonable
adverse environmental effect.
As part of this approach, EPA would
also require that any such information
be reported in connection with any
application to register a pesticide
product containing any nanoscale
material (40 CFR 152.50(f)(3)). As with
the reporting obligation under FIFRA
section 6(a)(2), EPA would consider the
failure to provide these types of
information with an application for a
product containing nanoscale material
to be a violation of FIFRA sections
12(a)(2)(B)(ii) and 12(a)(2)(N).
Agency regulations implementing
FIFRA section 6(a)(2) provide that a
registrant must submit information to
EPA that is reportable under section
6(a)(2) no later than the 30th calendar
day after the registrant first possesses or
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becomes aware of the information (40
CFR 159.155). In addition, a registrant is
required to submit to EPA any section
6(a)(2) information not explicitly
covered under the section 6(a)(2)
regulations if EPA has informed the
registrant that such additional
information has the potential to raise
questions about the continued
registration of a product or the
appropriate terms and conditions of
registration of a product (40 CFR
159.195).
After learning that EPA was
considering relying on FIFRA 6(a)(2) to
require reporting, some stakeholders
raised questions about the use of FIFRA
section 6(a)(2) to obtain this
information. Even though, as stated
above, EPA is not making a judgment
that the presence of any particular
nanoscale material poses a risk, it has
been argued that use of the ‘‘adverse
effects’’ reporting authority in FIFRA
section 6(a)(2) could create a ‘‘stigma’’
for the nanotechnology industry.
EPA does not believe that using
FIFRA section 6(a)(2) to gather
information on the presence of
nanoscale materials in pesticide
products would create a stigma for the
nanotechnology industry. EPA’s
longstanding interpretation of section
6(a)(2) is that it is not limited to
requiring reporting only of actual
‘‘adverse effects’’ of pesticides, and its
use does not imply that ‘‘adverse
effects’’ actually have occurred, or even
could occur, in connection with the
pesticide or pesticide ingredient on
which the information is being
obtained. FIFRA section 6(a)(2) requires
reporting of ‘‘additional factual
information regarding unreasonable
adverse effects on the environment,’’
where ‘‘unreasonable adverse effects on
the environment’’ is specifically defined
as a risk/benefit standard. EPA’s
implementing regulations require
reporting of a wide range of data,
which—like information on nanoscale
materials—are relevant to EPA’s risk/
benefit evaluations, but which do not
indicate the pesticide causes any
adverse effects. Any suggestion that this
information gathering proposal implied
an EPA position on the adverse effects
of pesticides containing nanoscale
materials would be a misinterpretation
of EPA’s intent.
It is further EPA’s position that
merely filing an additional report under
FIFRA section 6(a)(2) does not
stigmatize pesticides and would not
stigmatize any nanomaterials in
pesticides, since filing such reports is
quite common. On average, EPA
receives 200 studies and 56,000 incident
reports per year under this authority. In
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fact, over the last 10 years, pesticide
registrants have filed section 6(a)(2)
reports on more than two-thirds of all
pesticide active ingredients.
Use of FIFRA section 6(a)(2) also
would have only a minimal overall
administrative burden for both EPA and
industry. Under section 6(a)(2), only
registrants who know that their
products contain nanoscale materials
would be required to report to EPA.
Further, they would be required to
report only the information they know
about. Section 6(a)(2) does not require a
registrant to generate new data or to
seek out additional information.
Further, registrants and applicants
whose products do not contain
nanoscale materials (or who do not
know that their products contain
nanoscale materials) would have no
reporting obligation under FIFRA
section 6(a)(2). Under this approach,
EPA would be required to keep track of
each response received under 6(a)(2),
but would not otherwise need to
prepare or track individual requests for
the information.
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B. DCIs Under FIFRA Section 3(c)(2)(B)
As an alternative to relying on FIFRA
section 6(a)(2) to obtain information
concerning nanoscale materials in
pesticides, EPA is also considering
issuing DCIs under FIFRA section
3(c)(2)(B). The Agency has authority
under FIFRA section 3(c)(2)(B) to issue
a DCI notice to a pesticide registrant
directing them to provide data ‘‘required
to maintain in effect an existing
registration of a pesticide * * *’’ The
DCI notice is addressed to an individual
registrant, specifically identifies the
information or data that the registrant
must provide, prescribes an initial
response deadline of 90 days, and, if
data are to be generated, it may
prescribe a timeframe for generating and
providing that data. Under FIFRA, EPA
can suspend the registration of a
pesticide if the registrant fails to
respond to a DCI.
As part of this alternate approach,
EPA would also need to require the
inclusion of this information with any
application for registration of a pesticide
product that contains a nanoscale
material. EPA is reviewing whether this
could be done under existing
regulations or whether EPA would need
to amend existing regulations to clarify
that this information is required with
any application for registration. As with
the reporting obligation under FIFRA
section 6(a)(2), EPA would consider the
failure to provide these types of
information with an application for a
product containing nanoscale material
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to be a violation of FIFRA sections
12(a)(2)(B)(ii) and 12(a)(2)(N).
Since EPA’s goal is to identify what
nanoscale materials are contained in
products (and the products that contain
them) and to gather existing information
not previously provided to assess their
safety, the DCI would need to require
the kinds of information specified in
Unit IV. of this document. Because such
a request is not consistent with the Reregistration or Registration Review
programs, the Agency would use the
Enforcement and Unanticipated
Circumstances category available in the
currently approved Information
Collection Request (73 FR 55072,
September 24, 2008) (FRL–8719–3).
Unless a registrant has already
disclosed the presence of nanoscale
material in all of its products, there
currently is no way to identify with
certainty what nanoscale materials are
in products (and the products that
contain them). Therefore, in order to
identify what nanoscale materials are in
products, EPA could initially send an
individual Enforcement and
Unanticipated Circumstances DCI order
to each of the 1,716 currently registered
pesticide producers. Under this
approach each of these pesticide
registrants would then be required to
respond within 90 days by either
providing the requested information
about the nanoscale materials in their
product(s) or certifying that their
product(s) do not contain nanoscale
materials. In addition to keeping track of
each response like under FIFRA section
6(a)(2), the approach under FIFRA
section 3(c)(2)(B) could require EPA to
also prepare and track the issuance of
individual DCIs for each pesticide
registrant, as well as determine and take
any necessary enforcement actions for
non-responders. EPA notes that only
pesticide registrants receive DCIs; EPA
would need to employ additional
administrative procedures to ensure that
applicants also provided such
information.
A variation on this approach would
be for EPA to craft a DCI that would be
more targeted and place less burden on
industry and the Agency, possibly by
not requiring a response from recipients
of the DCI who do not have (or who do
not know that they have) nanoscale
material in their registered pesticide
products. The Agency has not used such
an approach with any DCI in the past;
however, and a number of issues,
including enforcement, would need to
be addressed if it were to seek to do so
here. EPA could also focus its initial
data gathering on certain classes of
pesticides that might be most likely to
contain a nanoscale material that EPA
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would be interested in knowing about.
EPA is interested in receiving comments
on these variations.
It is useful to note that while FIFRA
section 6(a)(2) can be used to obtain
existing information, the DCI approach
under FIFRA section 3(c)(2)(B) allows
the Agency to request that data be
generated. If EPA uses FIFRA section
6(a)(2) authority and the Agency learns,
for instance, the identity of a nanoscale
material present in a product, and
subsequently determines that sufficient
data are not available to support the
continued registration of the pesticide,
EPA could then use the DCI approach
under FIFRA section 3(c)(2)(B) to gather
such information. EPA must use the DCI
approach if EPA intends to require a
registrant to provide information which
the registrant does not already possess.
It is anticipated that some registrants
will request that EPA review
information to determine if their
product contains nanoscale materials.
To the extent that the description of
nanoscale material to a particular
product or ingredient is unclear, EPA
will review information concerning the
composition and manufacturing process
of the pesticide product and, based on
that information, the Agency will
determine whether the product does (or
does not) contain nanoscale material.
It has been suggested that the use of
a 3(c)(2)(B) approach would result in
submission of information that only
reflected the composition of registrants’
products at the time of their responses,
but that EPA would need periodically to
issue DCIs to ensure that registrants did
not alter the composition of the
products to add nanoscale materials
after submitting their responses. EPA is
interested in receiving comments on
options whereby it can ensure
registrants report what nanoscale
materials are in products, regardless of
when they are added to the pesticide.
Under either the 6(a)(2) or the
3(c)(2)(B) approach, DCIs targeted to
individual pesticide products that
contain specific nanoscale materials
would likely be used in the future to
collect more specific information or data
about particular products. EPA would
consider doing so on a case-by-case
basis and would tailor any request for
information accordingly.
C. Amending the Pesticide Data
Requirement Regulations
Some stakeholders have suggested, as
an alternative to relying on either FIFRA
section 6(a)(2) or 3(c)(2)(B) DCIs to
obtain information concerning
nanoscale materials in pesticides, that
EPA instead promulgate a regulation
amending the data requirements in 40
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CFR parts 158 and 161. The Agency
could amend the data requirements to
include disclosure of what nanoscale
materials are present as part of the
pesticide registration process. However,
completing this action would not
provide information on currently
registered pesticide products.
The Agency sees such proposed
rulemaking with a broader scope in that
it would address not only the basic
information such as identifying what
nanoscale materials are in products, but
also many other types of data required
for making safety evaluations. The
Agency is currently making data need
decisions on a case-by-case basis, and
EPA is trying to tailor data requirements
to the particular characteristics of each
product. The Agency does not yet have
the knowledge base typically gained
through the registration process to
support the development of specific
data requirements that would be
imposed broadly for the registration of
pesticides containing nanoscale
materials across all the application and
use scenarios, as required for such a
rulemaking.
Although it could take considerable
time to finalize and implement a rule
establishing standard data requirements
for pesticides containing nanoscale
materials, and the Agency thus believes
that this approach by itself would not
generate information on nanoscale
ingredients in pesticides in a timely
manner, EPA also seeks comment on
this approach.
VI. Proposed Policy Regarding
Classification of Applications Under
FIFRA and PRIA for Products
Containing Nanoscale Active and Inert
Ingredients
As discussed in more detail earlier in
this document, under FIFRA, all
pesticides must meet stringent statutory
and regulatory standards before they are
registered by the Agency and allowed to
be marketed and sold. Pesticides
containing nanoscale materials, whether
as active or inert ingredients, must meet
the same safety standards as other
pesticides. Because of the large and
increasing body of data described in
Unit III.B. of this document
demonstrating that size can alter the
manner in which materials behave and,
in turn, the potential risk to human
health and the environment associated
with such materials, EPA proposes to
apply an initial presumption that active
and inert ingredients, which are the
nanoscale versions of non-nanoscale
active and inert ingredients already
present in registered pesticide products,
are potentially different from those
conventionally sized counterparts.
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Because the size, shape, and other
characteristics of nanoscale ingredients
are likely to vary widely, EPA also
proposes to apply an initial
presumption that nanoscale active and
inert ingredients are potentially
different even from other, alreadyregistered nanoscale versions of the
same ingredients. As explained later in
this document, however, applicants can
overcome this presumption on a caseby-case basis.
Historically, EPA has evaluated an
application for registration of a pesticide
product that claims to have the same
composition and uses as a currently
registered pesticide—a so-called ‘‘metoo application’’—under either the
‘‘conditional’’ registration or
‘‘unconditional’’ registration authorities
in FIFRA section 3(c)(7) and section
3(c)(5), respectively. In making the
statutory determinations under section
3(c)(7)(A)—whether the applicant’s
product is identical or substantially
similar to a currently registered
pesticide or differs only in ways that
would not significantly increase the risk
of unreasonable adverse effects on the
environment, and that approving the
registration in the manner proposed
would not significantly increase the risk
of any unreasonable adverse effect on
the environment—EPA has focused on
whether the use patterns of the products
are identical or similar and whether the
ingredients present in the products have
the same chemical structure and are
present in about the same percentages.
Until recently, EPA generally has not
focused on the size of an ingredient as
an attribute relevant to making the
determinations under section 3(c)(7)(A).
As noted previously, however, once
the size of an ingredient is reduced
below approximately 100 nm, a
substance can exhibit different
properties, and therefore it may also
have different potential environmental
health and safety properties.
Accordingly, for a product containing
an ingredient that is a nanoscale version
of a conventionally sized active or inert
ingredient contained in an alreadyregistered product, EPA may require
additional data in order to determine
that the nanoscale material differs only
in ways that do not significantly
increase the risk of unreasonable
adverse effects on the environment and
that approving the registration in the
manner proposed would not
significantly increase the risk of any
unreasonable adverse effect on the
environment, and/or require different
terms and conditions for the
registration. EPA is thus proposing that
it not make the requisite findings absent
specific information on the nanoscale
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material included in a pesticide product
when the application relies on a
comparison to a currently registered
pesticide product containing either a
non-nanoscale version of the same
ingredient or another nanoscale version
of the ingredient that has different
characteristics. Under this approach, the
Agency would follow the same thinking
in making the statutorily required
determinations under FIFRA section
3(c)(7)(B) and 3(c)(7)(C), as well as
FIFRA section 3(c)(5).
For purposes of registration under
FIFRA section 3(c)(5) or 3(c)(7),
therefore, EPA would initially classify
any application for registration of a
pesticide product containing an active
or inert ingredient that is a nanoscale
material as an application for a ‘‘new’’
active or inert ingredient, even when
another registered pesticide product
contains a non-nanoscale form of the
ingredient or a nanoscale form of the
ingredient with different size
dimensions or other properties. This
initial presumption, however, could be
rebutted on a case-by-case basis through
the submission of, among other
possibilities, bridging data or other
information demonstrating to EPA’s
satisfaction that the nanoscale material’s
properties, which are relevant to
assessing the potential risks to human
health and the environment, are
substantially similar to the properties of
the already-registered non-nanoscale or
already-registered nanoscale form of the
material, or that the nanoscale material
differs only in ways that do not
significantly increase the risk of
unreasonable adverse effects on the
environment, and that approving the
registration in the manner proposed
would not significantly increase the risk
of any unreasonable adverse effect on
the environment.
If an applicant could make this
showing to EPA’s satisfaction, then the
application would be processed as a
‘‘me-too’’ application within the
timeframes prescribed for such
applications. However, if an applicant
could not make this showing to EPA’s
satisfaction, then EPA would process
such products as new active ingredients
or new inert ingredients and would
complete its review within the
timeframes prescribed for such
applications. In those circumstances,
the Agency would likely require the
applicant to provide the types of data
typically required for an assessment of
the potential hazards and exposure to a
new active or inert ingredient. Under
this proposed policy, it would also
follow that if a registrant wished to
change the composition of its product to
include a nanoscale version of a
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material that EPA had previously
approved in non-nanoscale form, the
registrant would need to notify EPA and
obtain EPA approval before making
such a change in the composition of its
product. However, as noted earlier, the
registration status of a product would
not change merely as a result of
providing information to EPA about the
presence of a previously-unreported
nanoscale material. If EPA made an
affirmative finding that a change in
status or conditions of use was
necessary, EPA would notify the
registrant in accordance with applicable
regulations and procedures.
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VII. Does this document contain
binding requirements?
This document seeks comments on
how the Agency could use FIFRA
section 6(a)(2) or FIFRA section
3(c)(2)(B) to gain information on what
nanoscale materials are in pesticides.
Given that the Agency is seeking
comment before determining its
approach to obtaining information on
what nanoscale materials are in
pesticides, there are no binding
requirements in this document.
Once this document is finalized, the
Agency’s policy for determining
whether a nanoscale material is a new
active or inert ingredient for purposes of
both FIFRA and PRIA would be
intended only as guidance to EPA
personnel and decision-makers and to
pesticide applicants. While the
requirements in the statute and Agency
regulations are binding on EPA and the
applicants, the proposed policy
described in this document would not
be binding on EPA personnel, pesticide
applicants, or the public. Accordingly,
EPA may depart from the policy
proposed herein if and when
circumstances warrant. Likewise,
pesticide applicants may assert that the
proposed policy is not applicable to a
specific pesticide or situation in which
EPA may be expected to apply it.
VIII. Questions for Comment
The Agency is seeking public
comment on several questions,
including whether it should use the
FIFRA section 6(a)(2) reporting
obligation to obtain information on what
nanoscale materials are in pesticide
products or use FIFRA section 3(c)(2)(B)
as described in this document to obtain
such information.
With respect to the scope of
reportable information, EPA specifically
invites comments on the following
issues:
1. In view of the Agency’s goal of
identifying what nanoscale materials are
in products so that EPA can determine
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whether it needs additional data to
evaluate the products’ safety under
FIFRA, should EPA change the
description of a ‘‘nanoscale material’’?
For example, should the size range
remain ‘‘between approximately 1 and
100 nm in one dimension’’? Are there
other characteristics that EPA should
consider, e.g., morphology, including
shape and crystal structure; surface
chemistry and reactivity; specific
surface area, charge; solubility;
conductive, magnetic, and optical
properties?
2. Should the reporting requirement
apply only to nanoscale material that is
‘‘intentionally produced to have at least
one dimension that measures between
approximately 1 and 100 nanometers,’’
or should it also apply to naturally
occurring materials? Why?
3. Is the meaning of ‘‘intentionally
produced’’ sufficiently clear? If not, in
what circumstances would the term be
unclear and how might it be clarified?
Would offering a consultation
procedure—by which a registrant or
applicant describes to EPA the
production process that results in the
presence of a material in the nanoscale
size range, and EPA responds with a
determination regarding whether
reporting is required—be an acceptable
approach to providing clarity?
4. Should the reporting requirement
apply to ingredients in pesticides that
contain any amount of a nanoscale
material, or should the requirement
apply only if an ingredient contains
more than a specified percentage (e.g.,
10%) of nanoscale material? If the latter,
what should the specified percentage be
and why?
5. How should the reporting
requirement apply to a pesticide
manufacturer who purchases
ingredients that may contain nanoscale
material?
6. Are there ways in which the
description of ‘‘nanoscale materials’’
can be refined and clarified, including
ways in which agglomeration and
aggregation could be considered as well
as suggestions for ways in which more
subjective criteria, such as ‘‘unique or
novel properties’’ can be incorporated
into the screening criteria?
7. Is EPA’s description of ‘‘nanoscale
material’’ inconsistent with other
definitions of nanoscale material or
similar terms? If so, please comment on
whether such differences create any
regulatory issues. In particular, does the
focus on ‘‘intentionally produced’’
materials create any such inconsistency
with other definitions of nanoscale
materials or similar terms?
8. If a pesticide is identified as
containing a particular nanoscale
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material, what would be the most useful
next steps to inform EPA’s
understanding of potential risks
associated with the pesticide? Are there
tests that could provide useful
information toward an understanding of
risk that would be common to all
nanoscale materials, or should the data
requirements necessarily be compoundand situation-specific? How should
bioavailability be considered in
determining testing requirements (e.g.,
are nano-particles respirable or bound to
other components)?
With respect to the proposed
approaches, EPA is seeking comment on
how to implement them to ensure
efficient, effective, and timely review of
applications. EPA specifically invites
comments on the following issues:
1. Is there a way to determine, in
advance of receiving an application for
registration of a product containing a
nanoscale material, whether a particular
kind of nanoscale material has
properties that, for purposes of risk
assessment, are essentially the same as
larger sized materials of the same
substance? If so, how would such
determinations be made and on what
would they be based?
2. What kinds of information should
EPA accept as demonstrating that a
pesticide product containing a
nanoscale ingredient is identical or
substantially similar to a currently
registered pesticide or differs only in
ways that would not significantly
increase the risk of unreasonable
adverse effects on the environment, and
that approving the registration in the
manner proposed would not
significantly increase the risk of any
unreasonable adverse effect on the
environment?
3. Can you suggest any alternative(s)
to the proposed approaches that would
be equally or even more effective in
addressing the status of nanoscale
materials as new active or inert
ingredients for purposes of both FIFRA
and PRIA, keeping in mind the data
showing that size, especially when
reduced below approximately 100 nm,
may alter the manner in which materials
behave and, in turn, the potential risk to
human health and the environment
associated with such materials?
With respect to the potential
alternative ways of obtaining the needed
information on what nanoscale
materials are in pesticide products, EPA
specifically invites comments on the
following issues:
1. Has EPA appropriately
characterized in this document the
current scientific understanding of the
potential risks of nanoscale materials? If
not, please comment on how to
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characterize the potential risks of
nanoscale materials. How would the
perception of the risks of nanoscale
materials differ depending on the
approach used by EPA to require
needed data on nanoscale materials in
pesticides? How could EPA lessen the
possibility that issuance of a final
requirement to report what nanoscale
materials are in pesticides will result in
a public misunderstanding of the
potential risks of nanotechnology more
generally?
2. Do commenters believe that
identification of the nanoscale materials
in pesticide products is relevant to
EPA’s statutory determination regarding
the potential for unreasonable adverse
effects on the environment? Please
provide the scientific or legal basis for
your view.
3. Has EPA characterized the
alternative approaches with respect to
which they would: (a) result in a
misunderstanding of the potential risks
posed by nanoscale materials; (b) result
in the timely submission of needed
information; and (c) impose burdens on
pesticide companies, those whose
products do, and do not, contain
nanoscale materials? If not, please
comment on those issues.
4. If EPA uses FIFRA section 6(a)(2)
to obtain the needed information on
nanoscale materials in pesticides, how
could the Agency ensure that its action
is not mischaracterized or
misunderstood as a determination that
the mere fact that a pesticide contains
nanoscale materials causes
unreasonable adverse environmental
effects?
5. If EPA were to use DCIs to obtain
the needed information on nanoscale
materials in pesticides, how could EPA
reduce both the burdens on registrants
and on EPA, as well as the time required
to complete such a process? For
example, is it possible to reduce the
burdens on registrants by targeting only
certain types of products? If so, how
would EPA determine which products
should receive DCIs?
6. What are the advantages and
disadvantages of requesting information
on nanoscale materials specifically
versus requesting information on size
distribution generally? (Note that either
type of information could be collected
under either the 6(a)(2) or the 3(c)(2)(B)
approach, except that 6(a)(2) cannot be
used to require the production of new
information that does not already exist,
while a collection under 3(c)(2)(B) must
be directed to an individual registrant
and requires a response.) Is identifying
what nanoscale materials are in
products a useful first step, or should
EPA move towards immediate
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collection of more specific information,
such as particle size distribution, on
products that might contain nanoscale
materials? Are there other physical and/
or chemical properties that might be
equally or more important for assessing
the potential of a pesticide to cause
unreasonable adverse effects on the
environment (e.g., morphology,
including shape and crystal structure;
surface chemistry and reactivity;
specific surface area, charge; solubility;
conductive, magnetic, and optical
properties)? Should information on
these properties be separately
requested? What would be the value and
burden of obtaining such information?
1. If EPA were to use rulemaking to
establish data requirements for
pesticides containing nanoscale
materials, what types of information
should EPA use to determine
appropriate data requirements? What
types of studies should EPA require to
evaluate a nanoscale material?
2. When choosing an approach for
obtaining needed data, how should EPA
weigh considerations relating to the
need to update its safety evaluations of
currently marketed pesticides in a
timely manner, the goal of ensuring
marketplace equity, and the interest in
minimizing the burdens on regulated
entities?
IX. References
As indicated under ADDRESSES, a
docket has been established for this
document under docket ID number
EPA–HQ–OPP–2010–0197. The
following is a listing of the documents
that are specifically referenced in this
document. The docket includes these
documents and other information
considered by EPA, including
documents that are referenced within
the documents that are included in the
docket, even if the referenced document
is not physically located in the docket.
For assistance in locating these other
documents, please consult the technical
contact person listed under FOR FURTHER
INFORMATION CONTACT.
¨
1. Oberdorster, G. et al. 2005.
Nanotoxicology: an emerging discipline
evolving from studies of ultrafine
particles. Environmental Health
Perspectives. (113):823–839.
2. National Nanotechnology Initiative. 2011.
Strategic Plan. https://www.nano.gov/
nnistrategicplan211.pdf.
3. Department of Health and Human
Services. Centers for Disease Control and
Prevention. National Institute for
Occupational Safety and Health.
Approaches to Safe Nanotechnology:
Managing the Health and Safety
Concerns Associated with Engineered
Nanomaterials. November 2009. https://
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www.cdc.gov/niosh/docs/2009-125/pdfs/
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4. SCENIHR. 2009. Risk Assessment of
Products of Nanotechnologies. European
Commission. Directorate-General for
Health and Consumers. Scientific
Committee on Emerging and Newly
Identified Risks, Brussels: 28th Plenary
Meeting. January 19, 2009. https://
ec.europa.eu/health/ph_risk/
committees/04_scenihr/docs/
scenihr_s_01.pdf.
5. Seaton, A. et al. 2010. Nanoparticles,
human health hazard and regulation. J.R.
Soc. Interface 7:S119–S129. https://
rsif.royalsocietypublishing.org/content/
early/2009/08/31/
rsif.2009.0252.focus.full#ref-14.
6. Wick, P. et al. 2009. Barrier Capacity of
Human Placenta for Nanosized
Materials. Environ. Health Perspect.
118:432–436.https://ehp.niehs.nih.gov/
members/2009/0901200/0901200.pdf.
7. Kim, Y.S. et al. 2008. Twenty-Eight Day
Oral Toxicity, Genotoxicity, and GenderRelated Tissue Distribution of Silver
Nanoparticles in Sprague-Dawley Rats.
Inhalation Toxicology. 20 (6):575–583.
8. Handy et al. 2008. The ecotoxicology and
chemistry of manufactured
nanoparticles. Ecotoxicology 17:287–
314.
9. Klaine et al. 2008. Nanomaterials in the
Environment: Behavior, Fate,
Bioavailability, and Effects. Environ.
Toxicol. Chem. 27: 1825–1851.
10. Federici et al. 2007. Toxicity of titanium
dioxide to rainbow trout (Oncorhynchus
mykiss): Gill injury, oxidative stress, and
other physiological effects. Aquat.
Toxicol. 84:415–430.
11. Smith et al. 2007. Toxicity of single
walled carbon nanotubes on rainbow
trout (Oncorhyncos mykiss): Respiratory
toxicity, organ pathologies, and other
physiological effects. Aquat. Toxicol.
82:94–109.
12. Lovern and Klaper. 2006. Daphnia magna
mortality when exposed to titanium
nanoparticles and fullerene (C60)
nanoparticles. Environ. Toxicol. Chem.
25:1132–1137.
13. Oberdorster et al. 2006. Ecotoxicology of
carbon-based engineered nanoparticles:
effects of fullerene (C–60) on aquatic
organisms. Carbon 44:1112–1120.
14. Roberts et al. 2007. In vivo
biomodification of lipidcoated carbon
nanotubes by Daphnia magna. Environ.
Sci. Technol. 41:3025–3029
15. Kashiwada et al. 2006. Distribution of
nanoparticles in the see-through Medaka
(Oryzias latipes). Environ. Health
Perspect. 114:1697–1702.
16. Cheng et al. 2007. Effect of carbon
nanotubes on developing zebrafish
(Danio rerio) embryos. Environ. Toxicol.
Chem. 26:708–716.
17. Kahru and Dubourguier. 2010. Review:
From ecotoxicology to
nanoecotoxicology. Toxicology 269:105–
119.
18. FIFRA Science Advisory Panel (SAP).
2010. ‘‘Evaluation of Hazard and
Exposure Associated with Nanosilver
and Other Nanometal Pesticide
E:\FR\FM\17JNP1.SGM
17JNP1
Federal Register / Vol. 76, No. 117 / Friday, June 17, 2011 / Proposed Rules
Products.’’ Report from the FIFRA
Scientific Advisory Panel Meeting of
November 2009. https://www.epa.gov/
scipoly/sap/meetings/2009/november/
110309ameetingminutes.pdf.
X. Applicable Statutory and Executive
Order Reviews
mstockstill on DSK4VPTVN1PROD with PROPOSALS
EPA submitted this document to the
Office of Management and Budget
(OMB) for review under Executive
Order 12866, entitled Regulatory
Planning and Review (58 FR 51735,
October 4, 1993). Any changes made in
response to OMB recommendations
have been documented in the docket for
this action as required by section
6(a)(3)(E) of the Executive Order.
The information collection
requirements associated with reporting
under FIFRA section 6(a)(2) as
prescribed in 40 CFR part 159, subpart
D are approved under the Paperwork
VerDate Mar<15>2010
17:37 Jun 16, 2011
Jkt 223001
Reduction Act (PRA), 44 U.S.C. 3501 et
seq. The approval is identified under
OMB Control No. 2070–0039 and EPA
ICR No. 1204. The information
collection requirements associated with
DCIs is approved under OMB Control
No. 2070–0174 and identified by EPA
ICR No. 2288. If EPA were to finalize a
policy that required additional reporting
of information not currently collected,
or that substantively changed the
burden for such reporting (for example
if it resulted in a larger number of such
reports than covered in current burden
estimates), EPA would submit a request
for revised PRA approval to OMB.
The various other statutory and
Executive Order review requirements
that apply to a regulatory action do not
apply to this action because this
document is not a regulatory action and
does not otherwise impose new
PO 00000
Frm 00045
Fmt 4702
Sfmt 9990
35395
requirements. As indicated previously,
this document requests comment on
several approaches for applying existing
requirements in order to obtain
information on nanoscale materials in
pesticide products and presents the
Agency’s proposed policy for
determining whether a nanoscale
material is a new active or inert
ingredient for purposes of both FIFRA
and PRIA.
List of Subjects
Environmental protection,
Administrative practice and procedure,
Nanotechnology, Pesticides and pests.
Dated: June 8, 2011.
Stephen A. Owens,
Assistant Administrator, Office of Chemical
Safety and Pollution Prevention.
[FR Doc. 2011–14943 Filed 6–16–11; 8:45 am]
BILLING CODE 6560–50–P
E:\FR\FM\17JNP1.SGM
17JNP1
Agencies
[Federal Register Volume 76, Number 117 (Friday, June 17, 2011)]
[Proposed Rules]
[Pages 35383-35395]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2011-14943]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Chapter I
[EPA-HQ-OPP-2010-0197; FRL-8877-9]
RIN 2070-ZA11
Pesticides; Policies Concerning Products Containing Nanoscale
Materials; Opportunity for Public Comment
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed policy statement.
-----------------------------------------------------------------------
SUMMARY: EPA seeks comment on several possible approaches for obtaining
information about what nanoscale materials are present in registered
pesticide products. Under one approach, EPA would use section 6(a)(2)
of the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA) to
obtain information regarding what nanoscale material is present in a
registered pesticide product and its potential effects on humans or the
environment. If EPA adopts this approach, 40 CFR 152.50(f)(3) would
also require the inclusion of such information with any application for
registration of a pesticide product that contains a nanoscale material.
Under an alternative approach, EPA would obtain such information using
Data Call-In notices (DCIs) under FIFRA section 3(c)(2)(B). If EPA
adopts this alternate approach, EPA would also
[[Page 35384]]
need to require the inclusion of this information with any application
for registration of a pesticide product that contains a nanoscale
material. It is EPA's view that FIFRA section 6(a)(2) is the most
efficient and expedient administrative approach to obtaining
information about nanoscale materials in pesticides and EPA would
prefer to use this approach. EPA is also proposing a new approach for
how EPA will determine on a case-by-case basis whether a nanoscale
active or inert ingredient is a ``new'' active or inert ingredient for
purposes of FIFRA and the Pesticide Registration Improvement Act
(PRIA), even when an identical, non-nanoscale form of the nanoscale
ingredient is already registered.
DATES: Comments must be received on or before July 18, 2011.
ADDRESSES: Submit your comments, identified by docket identification
(ID) number EPA-HQ-OPP-2010-0197, by one of the following methods:
Federal eRulemaking Portal: https://www.regulations.gov.
Follow the on-line instructions for submitting comments.
Mail: Office of Pesticide Programs (OPP) Regulatory Public
Docket (7502P), Environmental Protection Agency, 1200 Pennsylvania
Ave., NW., Washington, DC 20460-0001.
Delivery: OPP Regulatory Public Docket (7502P),
Environmental Protection Agency, Rm. S-4400, One Potomac Yard (South
Bldg.), 2777 S. Crystal Dr., Arlington, VA. Deliveries are only
accepted during the Docket Facility's normal hours of operation (8:30
a.m. to 4 p.m., Monday through Friday, excluding legal holidays).
Special arrangements should be made for deliveries of boxed
information. The Docket Facility telephone number is (703) 305-5805.
Instructions: Direct your comments to docket ID number EPA-HQ-OPP-
2010-0197. EPA's policy is that all comments received will be included
in the docket without change and may be made available on-line at
https://www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Do not submit information that you
consider to be CBI or otherwise protected through regulations.gov or e-
mail. The regulations.gov Web site is an ``anonymous access'' system,
which means EPA will not know your identity or contact information
unless you provide it in the body of your comment. If you send an e-
mail comment directly to EPA without going through regulations.gov,
your e-mail address will be automatically captured and included as part
of the comment that is placed in the docket and made available on the
Internet. If you submit an electronic comment, EPA recommends that you
include your name and other contact information in the body of your
comment and with any disk or CD-ROM you submit. If EPA cannot read your
comment due to technical difficulties and cannot contact you for
clarification, EPA may not be able to consider your comment. Electronic
files should avoid the use of special characters, any form of
encryption, and be free of any defects or viruses.
Docket: All documents in the docket are listed in the docket index
available at https://www.regulations.gov. Although listed in the index,
some information is not publicly available, e.g., CBI or other
information whose disclosure is restricted by statute. Certain other
material, such as copyrighted material, is not placed on the Internet
and will be publicly available only in hard copy form. Publicly
available docket materials are available either in the electronic
docket at https://www.regulations.gov, or, if only available in hard
copy, at the OPP Regulatory Public Docket in Rm. S-4400, One Potomac
Yard (South Bldg.), 2777 S. Crystal Dr., Arlington, VA. The hours of
operation of this Docket Facility are from 8:30 a.m. to 4 p.m., Monday
through Friday, excluding legal holidays. The Docket Facility telephone
number is (703) 305-5805.
FOR FURTHER INFORMATION CONTACT: Jed Costanza, Antimicrobials Division
(7510P), Office of Pesticide Programs, Environmental Protection Agency,
1200 Pennsylvania Ave., NW., Washington, DC 20460-0001; telephone
number: (703) 347-0204; fax number: (703) 308-8005; e-mail address:
costanza.jed@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. What is this document about?
This document describes several possible approaches for obtaining
certain additional information on the composition of pesticide
products. The notice focuses particularly on information about what
nanoscale materials are present in registered pesticide products. In
connection with this document, EPA describes ``nanoscale material'' as
an active or inert ingredient and any component parts thereof
intentionally produced to have at least one dimension that measures
between approximately 1 and 100 nanometers (nm).
Under one approach, EPA would use section 6(a)(2) of the Federal
Insecticide, Fungicide, and Rodenticide Act (FIFRA) to obtain
information regarding what nanoscale material is present in a
registered pesticide product and its potential effects on humans or the
environment. If EPA adopts this approach, 40 CFR 152.50(f)(3) would
also require the inclusion of such information with any application for
registration of a pesticide product that contains a nanoscale material.
Under an alternative approach, EPA would obtain such information
using Data Call-In notices (DCIs) under FIFRA section 3(c)(2)(B). If
EPA adopts this alternate approach, EPA would also need to require the
inclusion of this information with any application for registration of
a pesticide product that contains a nanoscale material. EPA is
reviewing whether this could be done under existing regulations or
whether EPA would need to amend existing regulations to clarify that
the information is required with any application for registration.
It is EPA's view that FIFRA section 6(a)(2) is the most efficient
and expedient administrative approach to obtaining information about
nanoscale materials in pesticides and EPA would prefer to use this
approach.
This document also proposes a new approach for how EPA will
determine on a case-by-case basis whether a nanoscale active or inert
ingredient is a ``new'' active or inert ingredient for purposes of
FIFRA and the Pesticide Registration Improvement Act (PRIA), even when
an identical, non-nanoscale form of the nanoscale ingredient is already
registered.
After considering any public comments on the use of FIFRA section
6(a)(2) or DCIs under FIFRA section 3(c)(2)(B), as well as public
comments submitted in response to other questions posed in this
document, EPA plans to issue a subsequent document in the Federal
Register announcing its approach to gather this information. EPA is
also asking for specific input on the proposed approach for determining
whether a nanoscale material is ``new'' under FIFRA and PRIA.
B. Does this action apply to me?
This action is directed to those persons who manufacture,
distribute, sell, apply, or regulate pesticide products, including
agricultural, commercial, and residential products (NAICS codes 32532
and 32561). 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
[[Page 35385]]
listed in this unit could also be affected. The North American
Industrial Classification System (NAICS) codes have been provided to
assist you and others in determining whether this action might apply to
certain entities. If you have any questions regarding the applicability
of this action to a particular entity, consult the person listed under
FOR FURTHER INFORMATION CONTACT.
C. What should I consider as I prepare my comments for EPA?
1. Submitting CBI. Do not submit this information to EPA through
regulations.gov or 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 ID number and other identifying
information (subject heading, Federal Register date and page number).
ii. Follow directions. The Agency may ask you to respond to
specific questions or organize comments by referencing a Code of
Federal Regulations (CFR) part or section number.
iii. Explain why you agree or disagree; suggest alternatives and
substitute language for your requested changes.
iv. Describe any assumptions and provide any technical information
and/or data that you used.
v. If you estimate potential costs or burdens, explain how you
arrived at your estimate in sufficient detail to allow for it to be
reproduced.
vi. Provide specific examples to illustrate your concerns and
suggest alternatives.
vii. Explain your views as clearly as possible.
viii. Make sure to submit your comments by the comment period
deadline identified.
II. Applicable Statutory and Regulatory Requirements
As a general matter, pesticides may not be sold or distributed in
the United States unless they are registered with EPA. FIFRA section
3(a) (7 U.S.C. 136a(a)). In order to obtain a pesticide registration,
an applicant must provide EPA with data (or cite existing data)
demonstrating that the proposed registration complies with the
requirement for registration. FIFRA section 3(c)(1)(F) (7 U.S.C.
136a(c)(1)(F)). FIFRA contains two provisions under which EPA may
register pesticides: Section 3(c)(5) for ``unconditional'' registration
and section 3(c)(7) for ``conditional'' registration (7 U.S.C.
136a(c)(5) and 7 U.S.C. 136a(c)(7)). Importantly, EPA must make
statutorily required findings for each and every pesticide product for
which registration is sought, regardless of whether another pesticide
product with the same or similar composition and use patterns is
already registered.
The standard for determining whether an application should be
granted unconditionally is found in FIFRA section 3(c)(5). This section
provides that, in order to grant a registration, EPA must find that a
product's composition warrants the proposed claims for it; that the
product's labeling and other material required to be submitted comply
with FIFRA; that the product will perform its intended function without
causing unreasonable adverse effects on the environment; and that, when
used in accordance with widespread and commonly recognized practice,
the product will not cause unreasonable adverse effects on the
environment.
FIFRA defines ``unreasonable adverse effects on the environment''
as including ``any unreasonable risk to man or the environment, taking
into account the economic, social, and environmental costs and benefits
of the use of any pesticide.'' FIFRA section 2(bb) (7 U.S.C. 136(bb)).
Thus, a critical aspect of determining whether or not a pesticide
product should be granted a registration is an evaluation of whether
the benefits associated with the use of a pesticide outweigh the risks
associated with such use. The burden of demonstrating that a product
meets the standards for registration rests at all times on the
registrant or applicant for registration. See, e.g., Industrial Union
Dept. v. American Petroleum Institute, 448 U.S. 607, 653 n. 61 (1980);
Environmental Defense Fund v. EPA, 510 F.2d 1292, 1297, 1302 (DC Cir.
1975).
The Agency has promulgated regulations in 40 CFR parts 158 and 161
which identify the types of data EPA expects an applicant to provide to
support an application for registration of a pesticide product. The
Agency requires a wide variety of studies in order to evaluate whether
a pesticide will cause unreasonable adverse effects on the environment.
These required studies include both toxicity tests and data to
characterize exposure to a pesticide, including extensive information
on a product's composition, and its fate in the environment and within
the human body. For certain pesticides EPA also requires data on
product efficacy.
If an applicant cannot provide necessary data for EPA to make the
determinations required to register a product unconditionally under
FIFRA section 3(c)(5), EPA may still be able to register the product
``conditionally'' under FIFRA section 3(c)(7). FIFRA section 3(c)(7)
authorizes EPA to register a pesticide product on the condition that
the applicant provides additional data necessary to support a finding
that the product meets the statutory standards in FIFRA section
3(c)(5). FIFRA section 3(c)(7) authorizes conditional registration in
three circumstances. First, the Agency may conditionally register a
product if EPA determines, among other things, that the product is
identical or substantially similar to a currently registered pesticide
or differs only in ways that would not significantly increase the risk
of unreasonable adverse effects on the environment, and that approving
the registration in the manner proposed would not significantly
increase the risk of any unreasonable adverse effect on the
environment. FIFRA section 3(c)(7)(A) (7 U.S.C. 136a(c)(7)(A)).
Products approved under this authority are commonly called ``me-too
registrations.'' Second, EPA may register a pesticide for an additional
use, if the applicant provides data to evaluate the safety of the new
use, and use of the product would not significantly increase the risk
of unreasonable adverse effects on the environment compared to products
already registered. FIFRA section 3(c)(7)(B) (7 U.S.C. 136a(c)(7)(B)).
These product approvals are referred to as ``new use'' registrations.
Finally, EPA may conditionally register a pesticide product that
contains an active ingredient not present in any currently registered
pesticide product, if the Administrator determines that:
1. The applicant has provided all data necessary to evaluate the
safety of the pesticide, with the exception of any data which are
lacking because the applicant has not had enough time to generate
the data since learning of the requirement;
2. Use of the pesticide during the time period needed to develop
the additional data will not cause unreasonable adverse effects on
the environment; and
[[Page 35386]]
3. Use of the pesticide is in the public interest.
FIFRA section 3(c)(7)(C) (7 U.S.C. 136a(c)(7)(C)).
As with applications for unconditional registrations, applicants
for conditional registration bear the burden at all times of
demonstrating that the statutory standards are met.
The Agency's interest in data to evaluate the risks and benefits of
a pesticide does not necessarily end once EPA has registered a
pesticide product. Accordingly, other provisions of FIFRA allow the
Agency to require pesticide registrants to develop and submit
information the Agency believes it needs in order to maintain the
registration of pesticide products.
A. DCI
Under FIFRA section 3(c)(2)(B), EPA may send a DCI notice to a
registrant requiring the registrant to provide additional data or other
information, which the registrant may need to generate or compile.
Specifically, ``if the Administrator determines that additional data
are required to maintain in effect an existing registration of a
pesticide, the Administrator shall notify all existing registrants of
the pesticide to which the determination relates and provide a list of
such registrants to any interested person.'' Failure to respond to the
DCI can serve as the basis for suspending the registration of the
product, thereby making it unlawful for the registrant to sell or
distribute the pesticide.
Generally, EPA's determination that additional data are needed is
contemplated to occur for one of the following five reasons:
1. The Re-registration Program. Section 4 of FIFRA requires EPA to
re-assess the health and safety data for all pesticide active
ingredients registered before November 1, 1984, to determine whether
these ``older'' pesticides meet the criteria for registration that
would be expected of a pesticide being registered today for the first
time. Section 4 of FIFRA directs EPA to use section 3(c)(2)(B)
authority to obtain the required data.
2. The Registration Review Program. Section 3(g) of FIFRA contains
provisions to help achieve the goal of reviewing each pesticide every
15 years to assure that the pesticide continues to pose no risk of
unreasonable adverse effects on human health or the environment.
Section 3(g) instructs EPA to use the section 3(c)(2)(B) authority to
obtain the required data.
3. Anticipated Residue/Percent Crop Treated Information. Under
section 408 of the Federal Food, Drug, and Cosmetic Act (FFDCA), before
a pesticide may be used on food or feed crops, the Agency must
establish a tolerance for the pesticide residues on that crop or
establish an exemption from the requirement to have a tolerance.
Section 408(b)(2)(E) and (F) of FFDCA authorize the use of anticipated
or actual residue (AR) data and percent crop treated (PCT) data to
establish, modify, maintain, or revoke a tolerance for a pesticide.
FFDCA requires that if AR data are used, data must be reviewed 5 years
after a tolerance is initially established.
4. The Special Review Program. EPA may conduct a Special Review if
EPA believes that a pesticide poses risks of unreasonable adverse
effects on human health or the environment. In the Special Review
Program, EPA focuses on specific hazards or uses of a pesticide.
Special Reviews are not intended to be comprehensive evaluations of the
pesticide; instead the Special Review DCIs are to address the specific
hazard or exposure concerns that are at issue.
5. Enforcement and Unanticipated Circumstances. The need for a DCI
may arise from the discovery of deficiencies in previously submitted
data, or from the discovery of specific attributes of the pesticide or
its ingredients. This may lead the Agency to determine that additional
information is necessary to reassess whether the pesticide will cause
unreasonable adverse effects on the environment. This type of DCI is
needed because the concern and therefore the need for data arise not
from a mandated review program like Re-registration or Registration
Review described above, but from unanticipated circumstances. Section
3(c)(2)(B) of FIFRA provides a means of obtaining any needed data.
B. FIFRA Section 6(a)(2)
FIFRA section 6(a)(2) provides that registrants must inform the
Agency of relevant information relating to their products, even though
it was not specifically requested by EPA. Specifically, FIFRA section
6(a)(2) requires that, ``[i]f at any time after the registration of a
pesticide the registrant has additional factual information regarding
unreasonable adverse effects on the environment of the pesticide, the
registrant shall submit such information to the Administrator.'' (7
U.S.C. 136d(a)(2)). For over 30 years, EPA has interpreted this
provision expansively to include not only information relating directly
to adverse effects caused by pesticides, but also to other types of
information and studies that EPA would typically use in assessing
whether a pesticide meets the statutory standard for registration
(i.e., the ``unreasonable adverse effects on the environment'' risk/
benefit standard). See 43 FR 37611 (August 23, 1978).
In 1997, EPA promulgated a final rule at 40 CFR part 159, subpart D
in the Federal Register issue of September 19, 1997 (62 FR 49370) (FRL-
5739-1), setting forth EPA's interpretation and enforcement policy
regarding FIFRA section 6(a)(2). The rule explains, among other things,
what information EPA regards as ``additional'' and ``factual,'' as well
as how quickly and to whom such information must be reported. The
regulation specifies many kinds of information, from varied scientific
disciplines, that EPA requires registrants to submit pursuant to FIFRA
section 6(a)(2). The types of information reflect the variety of
scientific data used by EPA in making the statutorily required
determinations--whether pesticides cause unreasonable adverse effects
on the environment. Thus, for example, the regulations generally
require registrants to report studies indicating that a pesticide
causes new or a higher incidence of toxic effects than previously
identified (see 40 CFR 159.165) and to report incidents involving
injury to humans, pets, or wildlife resulting from exposure to a
pesticide (40 CFR 159.184). But, EPA uses other types of information
that do not directly demonstrate adverse effects in its risk
assessments, and new factual information of this kind is also
reportable under the regulation. For example, registrants must report
studies that identify new metabolites, degradates, impurities, or
contaminants of pesticides (40 CFR 159.179); certain information on the
detection of pesticide residues in water, food, and feed (40 CFR
159.178); and new studies of human exposure (40 CFR 159.170). In sum,
EPA's regulation requires reporting of many types of information
relevant to EPA's assessment of the safety of a pesticide product--in
the words of section 6(a)(2) ``information regarding unreasonable
adverse effects on the environment of the pesticide''--not merely
information that directly concerns adverse effects.
In promulgating that regulation, however, EPA also recognized it
was impossible to establish rules addressing every type of factual
information that might become relevant in the future to judging whether
a registered pesticide product continued to meet the FIFRA statutory
standards. Accordingly, 40 CFR 159.195(a) provides:
[[Page 35387]]
The registrant shall submit to the Administrator information
other than that described in Sec. Sec. 159.165 through 159.188 if
the registrant knows, or reasonably should know, that if the
information should prove to be correct, EPA might regard the
information alone or in conjunction with other information about the
pesticide as raising concerns about the continued registration of a
product or about the appropriate terms and conditions of
registration of a product.
In addition, 40 CFR 159.195(c) provides that:
[t]he registrant shall submit * * * information other than that
described in Sec. Sec. 159.165 through 159.188 if the registrant
has been informed by EPA that such additional information has the
potential to raise questions about the continued registration of a
product or about the appropriate terms and conditions of
registration of a product.
Thus, once the Agency has informed registrants that EPA considers a
particular type of information relevant to determining whether a
pesticide has the potential to cause unreasonable adverse effects on
the environment, that type of information becomes reportable under
FIFRA section 6(a)(2).
Finally, EPA promulgated a regulation at 40 CFR part 152 addressing
the submission of applications for registration (53 FR 15952, May 4,
1988) (FRL-3266-9b). That rule specifies, among other things, certain
types of information that an application for registration of a
pesticide product must contain. The rule provides that the applicant
must ``furnish with his application any factual information of which he
is aware regarding unreasonable adverse effects of the pesticide on man
or the environment, which would be required to be reported under FIFRA
section 6(a)(2), if the product were registered.'' 40 CFR 152.50(f)(3).
Registrants' compliance with FIFRA section 6(a)(2) and EPA's
implementing regulations in 40 CFR parts 152 and 159 ensures that EPA
has access to any additional factual information that could be
important for determining whether a previous Agency decision to
register a pesticide remains a correct one, and whether a registered
pesticide can in fact be used without posing unreasonable adverse
effects to human health and the environment. This provision of FIFRA
recognizes that registrants may come into the possession of important
new information that was not anticipated by the Agency or of
information the importance of which was not previously known, and that
in the absence of registrants submitting such information, EPA might
well remain unaware of the information. Failures to report required
information, or delays in reporting, are regarded by EPA as violations
of FIFRA section 6(a)(2), which in turn makes them actionable under
FIFRA sections 12(a)(2)(B)(ii) and 12(a)(2)(N) (7 U.S.C.
136j(a)(2)(B)(ii) and 7 U.S.C. 136j(a)(2)(N)).
III. EPA's Interest in Nanoscale Materials as Pesticide Ingredients
EPA believes that certain information concerning pesticide
ingredients, which applicants and registrants have not routinely
provided previously, is relevant to the Agency's statutory obligation
to determine whether the registration of a pesticide may cause
unreasonable adverse effects on the environment. For the reasons
discussed below, EPA is particularly interested in nanoscale materials
in this context. Accordingly, EPA is considering how to collect
information about what nanoscale materials are in pesticide products
and is therefore soliciting public comment on two possible approaches.
It is important to first clarify how the term ``nanoscale material'' is
being used for purposes of this document.
A. Nanoscale Material
To date, EPA has not developed formal definitions for the terms
``nanotechnology'' or ``nanoscale materials'' or any similar terms for
regulatory purposes under any statute administered by the Agency. Broad
definitions for the terms ``nanotechnology'' or ``nanoscale materials''
and discussions of nanotechnology generally reflect the same common
elements, namely:
1. The material's particle size measures typically between
approximately 1 and 100 nm in at least one dimension;
2. The material exhibits unique or novel properties compared to
larger particles of the same material; and
3. Rather than occurring naturally, the material has been
manufactured or engineered at the nanoscale to take advantage of these
unique properties. See, for example, the definition from the National
Nanotechnology Initiative at: https://www.nano.gov/html/facts/whatIsNano.html.
These elements do not readily work in a regulatory context because
of the high degree of subjectivity involved with interpreting such
phrases as ``unique or novel properties'' or ``manufactured or
engineered to take advantage of these properties.'' Moreover, the
contribution of these subjective elements to risk has not been
established.
Instead, OPP will focus on more objective criteria in describing
when information about a ``nanoscale material'' in a pesticide product
may be relevant to determining whether the product has an unreasonable
adverse environmental effect. Specifically, such information may be
relevant in this context when the active or inert ingredient and any
component parts thereof is intentionally produced to have at least one
dimension that measures between approximately 1 and 100 nanometers,
regardless of the aggregation or agglomeration state of the final
material.
In determining whether an ingredient meets this description, EPA
may review particle size data and, among other things, the
manufacturing process to determine whether it employs processes
specifically to create or enhance the proportion of nanoscale materials
in the product, as compared with other processes used to produce
similar products. The Agency generally expects that these ingredients
may comprise, but are not limited to, metal-based (e.g., silver) and
carbon-based (e.g., carbon nanotubes) nanoscale materials. The Agency
does not, however, intend this description to cover biological
materials (e.g., DNA, RNA, proteins) or materials in their natural
state (e.g., clays). To the extent that the application of this
description to a particular product or ingredient is unclear, EPA would
review information provided by a registrant or applicant concerning the
composition of the pesticide product and to provide an Agency view on
whether the product did (or did not) contain a nanoscale material for
purposes of this policy.
B. Potential of Nanoscale Materials To Affect Human Health and the
Environment
There is a growing body of scientific evidence showing that
differences can exist between nanoscale material(s) and their non-
nanoscale counterpart(s) (Ref. 1). Nanoscale materials may have
different or enhanced properties--for example, electrical, chemical,
magnetic, mechanical, thermal, or optical properties--or features, such
as improved hardness or strength, that are highly desirable for
applications in commercial, medical, military, and environmental
sectors (Ref. 2). These properties are a direct consequence of small
size, which results in a larger surface area per unit of volume and/or
quantum effects that occur at the nanometer scale (i.e., 1 x 0-9
meters). Small size itself is also a desirable property of nanoscale
materials that is exploited for miniaturization of applications/
processes and/or
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stabilization or delivery of payloads to diverse environments or
incorporation into diverse products.
Nanoscale materials have a range of potentially beneficial public
and commercial applications, including medicine and public health,
clean energy through more efficient solar panels, pollution reduction
and environmental cleanup, and improved products such as stronger,
lighter, and more durable or conductive materials. These benefits arise
from the distinctive properties of nanoscale materials, in that they
are potentially more interactive or durable than other chemicals as a
result of their size and composition. EPA sees the emergence of
nanoscale materials as offering potential benefits for society in many
different fields, including pest control products. The use of nanoscale
materials in pesticide products and treated articles may allow for more
effective targeting of pests, use of smaller quantities of a pesticide,
and minimizing the frequency of spray-applied surface disinfection.
These could contribute to improved human and environmental safety and
could lower pest control costs. For example, as a materials
preservative, nanosilver should maintain its efficacy longer and
require smaller quantities than other silver preservatives due to an
expected gradual and controlled release of silver as opposed to the
rapid release of for example, silver from a zeolite structure or the
immediate dissolution of a silver salt. Therefore EPA seeks to
encourage innovative work in developing nanoscale materials to realize
these benefits.
However, a number of organizations have considered whether the
small size of nanoscale materials or the unique or enhanced properties
of nanoscale materials may, under specific conditions, pose new or
increased hazards to humans and the environment. Government, academic,
and private sector scientists in multiple countries are performing
research into the human health effects of diverse nanoscale materials,
resulting in a substantial and rapidly growing body of scientific
evidence. Recently, governmental and expert peer review organizations
have reviewed and summarized this evidence and offered views about the
implications of this evidence for environmental and human health and
safety.
For instance, in 2009, the National Institute of Occupational
Safety and Health (NIOSH) issued a report, ``Approaches to Safe
Nanotechnology: Managing the Health and Safety Concerns Associated with
Engineered Nanomaterials,'' which summarized the available scientific
information about nanoscale materials and identified the following
potential health and safety properties:
Nanomaterials have the greatest potential to enter the
body through the respiratory system if they are airborne and in the
form of respirable-sized particles (nanoparticles). They may also
come into contact with the skin or be ingested.
Based on results from human and animal studies,
airborne nanoparticles can be inhaled and deposit in the respiratory
tract; and based on animal studies, nanoparticles can enter the
bloodstream, and translocate to other organs.
Experimental studies in rats have shown that equivalent
mass doses of insoluble incidental nanoparticles are more potent
than large particles of similar composition in causing pulmonary
inflammation and lung tumors. Results from in vitro cell culture
studies with similar materials are generally supportive of the
biological responses observed in animals.
Experimental studies in animals, cell cultures, and
cell-free systems have shown that changes in the chemical
composition, crystal structure, and size of particles can influence
their oxidant generation properties and cytotoxicity.
Studies in workers exposed to aerosols of some
manufactured or incidental microscopic (fine) and nanoscale
(ultrafine) particles have reported adverse lung effects including
lung function decrements and obstructive and fibrotic lung diseases.
The implications of these studies to engineered nanoparticles, which
may have different particle properties, are uncertain.
Some nanomaterials may initiate catalytic reactions
depending on their composition and structure that would not
otherwise be anticipated based on their chemical composition. (Ref.
3).
Earlier the same year, the Scientific Committee on Emerging and
Newly Identified Health Risks (SCENIHR), an independent scientific
committee advising the European Commission's Health and Consumer
Directorate, issued a report, ``Risk assessment of products of
nanotechnologies.'' The SCENIHR report identified properties similar to
those identified in the NIOSH report:
Some specific hazards, discussed in the context of risk for
human health, have been identified. These include the possibility of
some nanoparticles to induce protein fibrillation, the possible
pathological effects caused by specific types of carbon nanotubes,
the induction of genotoxicity, and size effects in terms of
biodistribution.
and:
For some nanomaterials, toxic effects on environmental organisms
have been demonstrated, as well as the potential to transfer across
environmental species, indicating a potential for bioaccumulation in
species at the end of that part of the food chain.
(Ref. 4).
In another recent survey of scientific research on nanoscale
materials, the authors reported:
Many studies have examined the pro-inflammatory effects of
manufactured NPs [nanoparticles], on the basis that their ability to
cause inflammation is a major predictor of potential hazard in such
particles. The first important finding was that NPs have a more
pronounced effect on inflammation, cell damage and cell stimulation
than an equal mass of particles of the same material of greater size
[* * *]. This appears to hold true for materials as varied as carbon
black, titanium dioxide, various metals and polystyrene [* * *].
Surface area is the metric driving the pro-inflammatory effects and
this is evident both in vitro [* * *] and in vivo [* * *], particles
of various sizes producing inflammatory effects that are directly
related to the surface area dose.
(Ref. 5 [reference numbers in the original were omitted]).
Other reports in the scientific literature have indicated that some
nanoscale materials may cross the placental barrier (Ref. 6) or
translocate to diverse organs following oral exposure (Ref. 7). Once in
these diverse sites and organs, the large surface area of nanoscale
materials may facilitate increased reactivity and/or an inflammatory
response, resulting in toxic effects.
Two recent literature surveys describe a broad range of effects in
non-mammalian species following exposure to nanoscale materials (Refs.
8 and 9). These include, for example, increased ventilation rates,
mucus production, and pathologies, and related alteration of enzyme
activities and indicators of oxidative stress in rainbow trout,
Oncorhyncus mykiss (Refs. 10 and 11), and ingestion and accumulation of
nanoscale material in the digestive tract, as well as mortality,
increased heart rates, and reduced fecundity in Daphnia magna (Refs.
12, 13, and 14). Translocation of nano-scale materials from gill and
gut surface to blood and other organs in exposed Medaka, Oryzius
latipes, has also been reported (Ref. 15) and carbon nanotubes,
although unable to cross the egg surface, have been shown to delay
hatching in zebrafish, Danio rerio (Ref. 16). A recent review of lethal
effects and concentrations determined for a wide variety of species
showed that some nanoscale materials, including nano-titanium, nano-
zinc oxide, nano-silver, nano-copper oxide, C60, and single- and multi-
walled carbon nanotubes, would be classified as harmful to extremely
toxic to non-mammalian species (Ref. 17).
While the reports and articles cited previously have focused
primarily on
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differences between nanoscale material and conventionally sized
material of the same substances, EPA has also consulted with the FIFRA
Scientific Advisory Panel (SAP) on the extent to which different types
of nanoscale materials may display different properties. (The SAP is a
Federal advisory committee consisting of external, independent, expert,
scientific peer reviewers who provide advice to EPA on scientific
issues involved in the regulation of pesticides.) In response to EPA
questions on how size and other properties of nanoscale materials
potentially affect risk and how to assess such risks, the SAP said:
``Existing data clearly indicate that many properties of particles
change with size, including rate of release of ionic forms of metal,
reactivity or catalytic efficiency, Plasmon resonance, and quantum
effects. * * * The effect of particle size on biological responses to
particle exposure is less well defined.'' (Ref. 18). The SAP also noted
that ``[o]ther physicochemical properties, such as shape, charge and
surface coating, are also likely to impact biological response and
environmental fate [of nanoscale materials]. * * * The lack of a clear
understanding of how particle size and other physical properties affect
hazard profiles led most Panel members to be unsupportive of bridging
among silver-based materials with different properties.'' (Ref. 18).
It is important to emphasize that, while the conclusions described
previously apply to the specific material(s) and or context in which
the study was conducted, any individual type of nanoscale material may
not display all or even any of the characteristics observed and
reported for other nanoscale materials. In other words, some nanoscale
materials may have properties which, for purposes of assessing the risk
of a pesticide, are essentially identical to larger sized materials (or
particles) of the same substance. Furthermore, nanoscale materials may
also have properties that make them less risky, or more beneficial in
some other way, than larger sized materials (or particles) of the same
substance. So, it appears increasingly likely that there are few, if
any, universal ``nanoscale'' effects, and the distinctive effects seen
at nanoscale are specific to the properties of each material type under
specific exposure scenarios. Thus, EPA does not regard the fact that an
ingredient meets our description of a nanoscale material as evidence
that a pesticide containing the ingredient would cause unreasonable
adverse effects on the environment and thus would no longer meet the
statutory standards for registration. Rather, the presence of a
nanoscale material in a pesticide is grounds for EPA to consider the
possible need for data to characterize the potential of the ingredient
to pose risks. However, the registration status of a product would not
change merely as a result of providing information to EPA about the
presence of a previously-unreported nanoscale material. If, based on a
science based assessment of the risks of the specific pesticide
ingredients involved, EPA were to determine that the pesticide no
longer met the criteria for registration, or that some change was
needed in the conditions of use, EPA would conduct a separate action to
notify the manufacturer of that determination, consistent with current
FIFRA regulations.
Finally, scientifically speaking, there currently is no bright line
with respect to a size below (or above) which nanoscale materials do
(or do not) exhibit properties that might be of interest in assessing
whether a pesticide product has the potential to cause unreasonable
adverse effects on the environment. Therefore, the precise size range
in nanometers addressed by the policies proposed in this document might
be revised in the future as new information becomes available.
C. Nanoscale Materials and Pesticides
The Agency has information indicating that the use of
nanotechnology has started to expand into pesticide products, as it
already has in many other fields. For instance, a number of companies
have contacted EPA expressing an interest in obtaining registrations
for pesticide products containing ingredients identified as nanosilver
or nanosilver composite structures (jointly referred to as
``nanosilver''), and several companies have submitted applications to
register pesticides containing nanosilver. In addition, EPA now has
information suggesting that there are other pesticide products
currently registered and in the marketplace that contain nanosilver as
an active ingredient.
In order for EPA to fulfill its responsibilities to regulate
pesticides under FIFRA, it needs to determine whether pesticidal
products meet the statutory standards for registration. As summarized
previously, EPA believes that what intentionally produced nanoscale
materials are in a pesticide product, whether as an active or inert
ingredient, is relevant to that determination. Accordingly, EPA is
considering how to collect information not only about what nanoscale
materials are in pesticide products, but also other information that
may be relevant to the assessment of the potential of such pesticide
products to cause unreasonable adverse effects on the environment. Such
information may be important for EPA to determine whether EPA should
continue the registration of a product, or amend, as appropriate, the
terms and conditions of registration of a product. EPA is therefore
soliciting public comment on two possible approaches for obtaining this
information, as discussed in this document.
IV. Information Relevant To Assessing the Presence of Nanoscale
Materials in a Pesticide
In light of the foregoing and in consideration of the potential for
nanoscale material to cause different effects and to behave differently
in the environment and within organisms from larger particles of the
same substance, as well as from nanoscale materials with different
characteristics (see Unit III.B.), EPA believes that any of the
following types of information are relevant to assessing the potential
of a pesticide to cause unreasonable adverse effects on the
environment:
Any information concerning what nanoscale materials are
present in pesticides, whether as an active ingredient or as an inert
ingredient;
For any pesticide product that contains nanoscale
material, whether active or inert, any existing information that
characterizes the size and size distribution of the nanoscale material
as measured in nanometers;
For any pesticide product that contains nanoscale
materials, whether active or inert, any existing information that
describes the manufacturing process used to produce the nanoscale
material in whatever size range it is produced;
For any pesticide product that contains nanoscale
materials, whether active or inert, and that also is or will be used
for an end-use formulation that contain(s) a composite (e.g., the
active ingredient is a matrix complex comprised of the nanoscale
material(s) in combination with a carrier, such as silica or sulfur),
any existing information that characterizes the size and size
distribution of the composite; and
For any pesticide product that contains nanoscale
materials, whether active or inert, any existing information that shows
adverse effects at any level of exposure to the nanoscale material on
humans or nontarget species, and/or that shows the levels or nature
(e.g. routes, frequency, or life stage) of
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potential human and environmental exposure.
Importantly, the foregoing is not intended to be an exclusive list.
To the extent that a registrant has a pesticide product that contains a
nanoscale material, and in addition has any other existing information
not captured in the previous list that pertains to, concerns, or
otherwise relates to the nanoscale material and has the potential to
raise questions about the continued registration of a product or the
appropriate terms and conditions of a product registration, EPA is also
considering whether this too should be submitted to the Agency.
EPA will review information submitted concerning what nanoscale
materials are present, including any existing information not
previously provided to the Agency on size and size distribution,
manufacturing process, and adverse effects. EPA will use this and
product use information to determine if it raises any issues, not
previously considered, regarding the product's potential to cause
unreasonable adverse effects on the environment. In some cases, EPA may
determine that additional information is needed to assess such
potential; in this case, additional data may be required including data
on physical and chemical properties, rate of nanoscale material
release, and acute, subchronic, and chronic toxicity to human and
ecological receptors.
V. Reporting the Presence of Nanoscale Materials in Pesticide Products
As discussed in Units III. and IV. of this document, EPA believes
that information about what nanoscale materials are in pesticide
products is important to its assessment of whether pesticides meet the
statutory standard for registration. EPA may require such information
under either FIFRA section 6(a)(2) or section 3(c)(2)(B). The Agency
believes that announcing the applicability of FIFRA section 6(a)(2) to
this type of information would be the most efficient and expedient
administrative approach to obtaining existing information about
nanoscale materials in pesticides, in which case any registrants with
this type of information would be required to report it to EPA. The
Agency is considering, however, an alternative approach under which it
would issue DCIs under FIFRA section 3(c)(2)(B) to obtain this
information, in which case registrants that received the DCI would be
required to respond. This unit of the document discusses the two
possible approaches and related procedures for obtaining information
concerning nanoscale materials in pesticides.
A. FIFRA Section 6(a)(2)
As mentioned previously, FIFRA section 6(a)(2) and implementing
regulations in 40 CFR part 159 require pesticide registrants to report
certain information if that information:
1. Is additional;
2. Is factual; and
3. Regards unreasonable adverse effects on the environment of the
pesticide.
Per 40 CFR 159.195, this includes information that, if correct, a
registrant knows, or reasonably should know, would be regarded by EPA,
either alone or in conjunction with other information about the
pesticide, as raising concerns about the continued registration of a
product or about the appropriate terms and conditions of registration
of a product.
Announcing the applicability of FIFRA section 6(a)(2) to
information about nanoscale materials in pesticides would not mean that
EPA is expanding its interpretation of FIFRA section 6(a)(2) or
changing its regulations. Rather, consistent with EPA's section 6(a)(2)
regulations, EPA would be merely identifying a set of information that
adds to the subset of reportable section 6(a)(2) data explicitly
identified at present under the section 6(a)(2) regulations.
Further, the Agency notes that the identification of information as
reportable under FIFRA section 6(a)(2) does not mean that any
particular pesticide or group of pesticides, to which such information
pertains, poses a risk. Rather, the requirement merely indicates that
EPA has determined that a particular type of information is relevant
to, and may improve the Agency's ability to assess, whether the
pesticide would cause an unreasonable adverse environmental effect.
As part of this approach, EPA would also require that any such
information be reported in connection with any application to register
a pesticide product containing any nanoscale material (40 CFR
152.50(f)(3)). As with the reporting obligation under FIFRA section
6(a)(2), EPA would consider the failure to provide these types of
information with an application for a product containing nanoscale
material to be a violation of FIFRA sections 12(a)(2)(B)(ii) and
12(a)(2)(N).
Agency regulations implementing FIFRA section 6(a)(2) provide that
a registrant must submit information to EPA that is reportable under
section 6(a)(2) no later than the 30th calendar day after the
registrant first possesses or becomes aware of the information (40 CFR
159.155). In addition, a registrant is required to submit to EPA any
section 6(a)(2) information not explicitly covered under the section
6(a)(2) regulations if EPA has informed the registrant that such
additional information has the potential to raise questions about the
continued registration of a product or the appropriate terms and
conditions of registration of a product (40 CFR 159.195).
After learning that EPA was considering relying on FIFRA 6(a)(2) to
require reporting, some stakeholders raised questions about the use of
FIFRA section 6(a)(2) to obtain this information. Even though, as
stated above, EPA is not making a judgment that the presence of any
particular nanoscale material poses a risk, it has been argued that use
of the ``adverse effects'' reporting authority in FIFRA section 6(a)(2)
could create a ``stigma'' for the nanotechnology industry.
EPA does not believe that using FIFRA section 6(a)(2) to gather
information on the presence of nanoscale materials in pesticide
products would create a stigma for the nanotechnology industry. EPA's
longstanding interpretation of section 6(a)(2) is that it is not
limited to requiring reporting only of actual ``adverse effects'' of
pesticides, and its use does not imply that ``adverse effects''
actually have occurred, or even could occur, in connection with the
pesticide or pesticide ingredient on which the information is being
obtained. FIFRA section 6(a)(2) requires reporting of ``additional
factual information regarding unreasonable adverse effects on the
environment,'' where ``unreasonable adverse effects on the
environment'' is specifically defined as a risk/benefit standard. EPA's
implementing regulations require reporting of a wide range of data,
which--like information on nanoscale materials--are relevant to EPA's
risk/benefit evaluations, but which do not indicate the pesticide
causes any adverse effects. Any suggestion that this information
gathering proposal implied an EPA position on the adverse effects of
pesticides containing nanoscale materials would be a misinterpretation
of EPA's intent.
It is further EPA's position that merely filing an additional
report under FIFRA section 6(a)(2) does not stigmatize pesticides and
would not stigmatize any nanomaterials in pesticides, since filing such
reports is quite common. On average, EPA receives 200 studies and
56,000 incident reports per year under this authority. In
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fact, over the last 10 years, pesticide registrants have filed section
6(a)(2) reports on more than two-thirds of all pesticide active
ingredients.
Use of FIFRA section 6(a)(2) also would have only a minimal overall
administrative burden for both EPA and industry. Under section 6(a)(2),
only registrants who know that their products contain nanoscale
materials would be required to report to EPA. Further, they would be
required to report only the information they know about. Section
6(a)(2) does not require a registrant to generate new data or to seek
out additional information. Further, registrants and applicants whose
products do not contain nanoscale materials (or who do not know that
their products contain nanoscale materials) would have no reporting
obligation under FIFRA section 6(a)(2). Under this approach, EPA would
be required to keep track of each response received under 6(a)(2), but
would not otherwise need to prepare or track individual requests for
the information.
B. DCIs Under FIFRA Section 3(c)(2)(B)
As an alternative to relying on FIFRA section 6(a)(2) to obtain
information concerning nanoscale materials in pesticides, EPA is also
considering issuing DCIs under FIFRA section 3(c)(2)(B). The Agency has
authority under FIFRA section 3(c)(2)(B) to issue a DCI notice to a
pesticide registrant directing them to provide data ``required to
maintain in effect an existing registration of a pesticide * * *'' The
DCI notice is addressed to an individual registrant, specifically
identifies the information or data that the registrant must provide,
prescribes an initial response deadline of 90 days, and, if data are to
be generated, it may prescribe a timeframe for generating and providing
that data. Under FIFRA, EPA can suspend the registration of a pesticide
if the registrant fails to respond to a DCI.
As part of this alternate approach, EPA would also need to require
the inclusion of this information with any application for registration
of a pesticide product that contains a nanoscale material. EPA is
reviewing whether this could be done under existing regulations or
whether EPA would need to amend existing regulations to clarify that
this information is required with any application for registration. As
with the reporting obligation under FIFRA section 6(a)(2), EPA would
consider the failure to provide these types of information with an
application for a product containing nanoscale material to be a
violation of FIFRA sections 12(a)(2)(B)(ii) and 12(a)(2)(N).
Since EPA's goal is to identify what nanoscale materials are
contained in products (and the products that contain them) and to
gather existing information not previously provided to assess their
safety, the DCI would need to require the kinds of information
specified in Unit IV. of this document. Because such a request is not
consistent with the Re-registration or Registration Review programs,
the Agency would use the Enforcement and Unanticipated Circumstances
category available in the currently approved Information Collection
Request (73 FR 55072, September 24, 2008) (FRL-8719-3).
Unless a registrant has already disclosed the presence of nanoscale
material in all of its products, there currently is no way to identify
with certainty what nanoscale materials are in products (and the
products that contain them). Therefore, in order to identify what
nanoscale materials are in products, EPA could initially send an
individual Enforcement and Unanticipated Circumstances DCI order to
each of the 1,716 currently registered pesticide producers. Under this
approach each of these pesticide registrants would then be required to
respond within 90 days by either providing the requested information
about the nanoscale materials in their product(s) or certifying that
their product(s) do not contain nanoscale materials. In addition to
keeping track of each response like under FIFRA section 6(a)(2), the
approach under FIFRA section 3(c)(2)(B) could require EPA to also
prepare and track the issuance of individual DCIs for each pesticide
registrant, as well as determine and take any necessary enforcement
actions for non-responders. EPA notes that only pesticide registrants
receive DCIs; EPA would need to employ additional administrative
procedures to ensure that applicants also provided such information.
A variation on this approach would be for EPA to craft a DCI that
would be more targeted and place less burden on industry and the
Agency, possibly by not requiring a response from recipients of the DCI
who do not have (or who do not know that they have) nanoscale material
in their registered pesticide products. The Agency has not used such an
approach with any DCI in the past; however, and a number of issues,
including enforcement, would need to be addressed if it were to seek to
do so here. EPA could also focus its initial data gathering on certain
classes of pesticides that might be most likely to contain a nanoscale
material that EPA would be interested in knowing about. EPA is
interested in receiving comments on these variations.
It is useful to note that while FIFRA section 6(a)(2) can be used
to obtain existing information, the DCI approach under FIFRA section
3(c)(2)(B) allows the Agency to request that data be generated. If EPA
uses FIFRA section 6(a)(2) authority and the Agency learns, for
instance, the identity of a nanoscale material present in a product,
and subsequently determines that sufficient data are not available to
support the continued registration of the pesticide, EPA could then use
the DCI approach under FIFRA section 3(c)(2)(B) to gather such
information. EPA must use the DCI approach if EPA intends to require a
registrant to provide information which the registrant does not already
possess.
It is anticipated that some registrants will request that EPA
review information to determine if their product contains nanoscale
materials. To the extent that the description of nanoscale material to
a particular product or ingredient is unclear, EPA will review
information concerning the composition and manufacturing process of the
pesticide product and, based on that information, the Agency will
determine whether the product does (or does not) contain nanoscale
material.
It has been suggested that the use of a 3(c)(2)(B) approach would
result in submission of information that only reflected the composition
of registrants' products at the time of their responses, but that EPA
would need periodically to issue DCIs to ensure that registrants did
not alter the composition of the products to add nanoscale materials
after submitting their responses. EPA is interested in receiving
comments on options whereby it can ensure registrants report what
nanoscale materials are in products, regardless of when they are added
to the pesticide.
Under either the 6(a)(2) or the 3(c)(2)(B) approach, DCIs targeted
to individual pesticide products that contain specific nanoscale
materials would likely be used in the future to collect more specific
information or data about particular products. EPA would consider doing
so on a case-by-case basis and would tailor any request for information
accordingly.
C. Amending the Pesticide Data Requirement Regulations
Some stakeholders have suggested, as an alternative to relying on
either FIFRA section 6(a)(2) or 3(c)(2)(B) DCIs to obtain information
concerning nanoscale materials in pesticides, that EPA instead
promulgate a regulation amending the data requirements in 40
[[Page 35392]]
CFR parts 158 and 161. The Agency could amend the data requirements to
include disclosure of what nanoscale materials are present as part of
the pesticide registration process. However, completing this action
would not provide information on currently registered pesticide
products.
The Agency sees such proposed rulemaking with a broader scope in
that it would address not only the basic information such as
identifying what nanoscale materials are in products, but also many
other types of data required for making safety evaluations. The Agency
is currently making data need decisions on a case-by-case basis, and
EPA is trying to tailor data requirements to the particular
characteristics of each product. The Agency does not yet have the
knowledge base typically gained through the registration process to
support the development of specific data requirements that would be
imposed broadly for the registration of pesticides containing nanoscale
materials across all the application and use scenarios, as required for
such a rulemaking.
Although it could take considerable time to finalize and implement
a rule establishing standard data requirements for pesticides
containing nanoscale materials, and the Agency thus believes that this
approach by itself would not generate information on nanoscale
ingredients in pesticides in a timely manner, EPA also seeks comment on
this approach.
VI. Proposed Policy Regarding Classification of Applications Under
FIFRA and PRIA for Products Containing Nanoscale Active and Inert
Ingredients
As discussed in more detail earlier in this document, under FIFRA,
all pesticides must meet stringent statutory and regulatory standards
before they are registered by the Agency and allowed to be marketed and
sold. Pesticides containing nanoscale materials, whether as active or
inert ingredients, must meet the same safety standards as other
pesticides. Because of the large and increasing body of data described
in Unit III.B. of this document demonstrating that size can alter the
manner in which materials behave and, in turn, the potential risk to
human health and the environment associated with such materials, EPA
proposes to apply an initial presumption that active and inert
ingredients, which are the nanoscale versions of non-nanoscale active
and inert ingredients already present in registered pesticide products,
are potentially different from those conventionally sized counterparts.
Because the size, shape, and other characteristics of nanoscale
ingredients are likely to vary widely, EPA also proposes to apply an
initial presumption that nanoscale active and inert ingredients are
potentially different even from other, already-registered nanoscale
versions of the same ingredients. As explained later in this document,
however, applicants can overcome thi