Bacteriophage of Clavibacter Michiganensis Subspecies Michiganensis; Exemption From the Requirement of a Tolerance, 66187-66192 [2011-27042]
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Federal Register / Vol. 76, No. 207 / Wednesday, October 26, 2011 / Rules and Regulations
more flexible staffing may be the most
rational option.
Authority: 39 U.S.C. 101, 401, 403, 404,
410, 1001.
II. Explanation of Changes From
Proposed Rule
■
The final rule includes the following
additional changes to the proposed rule.
Paragraph 241.1(a) has been revised to
clarify that the operation or staffing of
a Post Office by non-postmaster
personnel must be at the direction of the
postmaster, and that it may include
times when the postmaster is not
physically present. While the proposed
rule referred to whether a Post Office
was ‘‘operated or managed’’ by nonpostmaster personnel, the phrase
‘‘operated or staffed’’ better reflects the
intended meaning that a postmaster
would continue to manage operations at
the Post Office, albeit possibly without
personally operating or staffing it on a
continuous basis.
A sentence is added to paragraph
241.3(a)(1)(ii) (redesignated as
241.3(a)(1)(iii)) to clarify that these
regulations will no longer apply to
discontinuance actions pending as of
December 1, 2011, that pertain to the
conversion of a Post Office to another
type of USPS-operated facility.
The definition of ‘‘consolidation’’ in
paragraph 241.3(a)(2)(iv) is revised to
restrict the term’s definition to instances
where a Postal Service-operated retail
facility is replaced with a contractoroperated retail facility that reports to a
Postal Service-operated retail facility.
Consistent with the proposed rule, the
term no longer encompasses situations
where a Post Office is replaced with a
Classified Station or Classified Branch.
Paragraph 241.3(b)(4) is revised to
indicate the possibility that a
consolidated facility’s name, or a similar
name, can be used by the succeeding
facility, rather than suggesting an
expectation that the former name will be
maintained, thereby allowing for the
range of contract- and service-specific
circumstances that can affect such a
determination.
The Postal Service hereby adopts the
following changes to 39 CFR part 241.
§ 241.1
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Organization and functions
(government agencies), Postal Service.
Accordingly, 39 CFR part 241 is
amended as follows:
PART 241—RETAIL ORGANIZATION
AND ADMINISTRATION:
ESTABLISHMENT, CLASSIFICATION,
AND DISCONTINUANCE
1. The authority citation for 39 CFR
part 241 continues to read as follows:
■
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(a) Establishment. Post Offices are
established and maintained at locations
deemed necessary to ensure that regular
and effective postal services are
available to all customers within
specified geographic boundaries. A Post
Office may be operated or staffed by a
postmaster or by another type of postal
employee at the direction of the
postmaster, including when the
postmaster is not physically present.
*
*
*
*
*
■ 3. In § 241.3:
■ a. Paragraph (a)(1)(i)(B) is revised;
■ b. Paragraph (a)(1)(ii) is redesignated
as paragraph (a)(1)(iii), and new
paragraph (a)(1)(ii) is added;
■ c. Newly redesignated paragraph
(a)(1)(iii) is revised;
■ d. Paragraph (a)(2)(iv) is revised;
■ e. Paragraph (b)(2)(i) is revised;
■ f. Paragraph (b)(4) is revised; and
■ g. Paragraph (c)(2) is revised.
The revisions and additions read as
follows:
(iv) ‘‘Consolidation’’ means an action
that converts a Postal Service-operated
retail facility into a contractor-operated
retail facility. The resulting contractoroperated retail facility reports to a Postal
Service-operated retail facility.
*
*
*
*
*
(b) * * *
(2) * * *
(i) In a consolidation, the ZIP Code for
the replacement contractor-operated
retail facility is the ZIP Code originally
assigned to the discontinued facility.
*
*
*
*
*
(4) Name of facility established by
consolidation. If a USPS-operated retail
facility is consolidated by establishing
in its place a contractor-operated
facility, the replacement unit can be
given the same name of the facility that
is replaced, if appropriate in light of the
nature of the contract and level of
service provided.
(c) * * *
(2) Consolidation. The proposed
action may include a consolidation of
USPS-operated retail facilities. A
consolidation arises when a USPSoperated retail facility is replaced with
a contractor-operated retail facility.
*
*
*
*
*
§ 241.3 Discontinuance of USPS-operated
retail facilities.
Stanley F. Mires,
Attorney, Legal Policy and Legislative Advice.
(a) * * *
(1) * * *
(i) * * *
(B) Combine a USPS-operated Post
Office, station, or branch with another
USPS-operated retail facility, or
(ii) The conversion of a Post Office
into, or the replacement of a Post Office
with, another type of USPS-operated
retail facility is not a discontinuance
action subject to this section. A change
in the staffing of a Post Office such that
it is staffed only part-time by a
postmaster, or not staffed at all by a
postmaster, but rather by another type of
USPS employee, is not a discontinuance
action subject to this section.
(iii) The regulations in this section are
mandatory only with respect to
discontinuance actions for which initial
feasibility studies have been initiated on
or after July 14, 2011. Unless otherwise
provided by responsible personnel, the
rules under § 241.3 as in effect prior to
July 14, 2011 shall apply to
discontinuance actions for which initial
feasibility studies have been initiated
prior to July 14, 2011. Discontinuance
actions pending as of December 1, 2011,
that pertain to the conversion of a Post
Office to another type of USPS-operated
facility are no longer subject to these
regulations.
(2) * * *
[FR Doc. 2011–27641 Filed 10–25–11; 8:45 am]
2. In § 241.1, paragraph (a) is revised
to read as follows:
List of Subjects in 39 CFR Part 241
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BILLING CODE 7710–12–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2009–0538; FRL–8891–3]
Bacteriophage of Clavibacter
Michiganensis Subspecies
Michiganensis; Exemption From the
Requirement of a Tolerance
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
This regulation establishes an
exemption from the requirement of a
tolerance for residues of lytic
bacteriophage of Clavibacter
michiganensis subspecies
michiganensis produced in Clavibacter
michiganensis subspecies
michiganensis in or on tomato when
applied as a bactericide in accordance
with good agricultural practices. On
behalf of OmniLytics, Inc., Interregional
Research Project Number 4 (IR–4)
submitted a petition to EPA under the
Federal Food, Drug, and Cosmetic Act
(FFDCA) requesting an exemption from
SUMMARY:
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Federal Register / Vol. 76, No. 207 / Wednesday, October 26, 2011 / Rules and Regulations
the requirement of a tolerance. This
regulation eliminates the need to
establish a maximum permissible level
for residues of lytic bacteriophage of
Clavibacter michiganensis subspecies
michiganensis produced in Clavibacter
michiganensis subspecies
michiganensis under the FFDCA.
DATES: This regulation is effective
October 26, 2011. Objections and
requests for hearings must be received
on or before December 27, 2011, and
must be filed in accordance with the
instructions provided in 40 CFR part
178 (see also Unit I.C. of the
SUPPLEMENTARY INFORMATION).
ADDRESSES: EPA has established a
docket for this action under docket
identification (ID) number EPA–HQ–
OPP–2009–0538. 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., Confidential Business Information
(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 in the electronic docket at
https://www.regulations.gov, or, if only
available in hard copy, at the Office of
Pesticide Programs (OPP) Regulatory
Public Docket in Rm. S–4400, One
Potomac Yard (South Bldg.), 2777 S.
Crystal Dr., Arlington, VA. The Docket
Facility is open 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:
Denise Greenway, Biopesticides and
Pollution Prevention Division (7511P),
Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001; telephone number:
(703) 308–8263; e-mail address:
greenway.denise@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
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A. Does this action apply to me?
You may be potentially affected by
this action if you are an agricultural
producer, food manufacturer, or
pesticide manufacturer. Potentially
affected entities may include, but are
not limited to:
• Crop production (NAICS code 111).
• Animal production (NAICS code
112).
• Food manufacturing (NAICS code
311).
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• Pesticide manufacturing (NAICS
code 32532).
This listing is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
affected by this action. Other types of
entities not listed in this unit could also
be affected. The North American
Industrial Classification System
(NAICS) codes have been provided to
assist you and others in determining
whether this action might apply to
certain entities. If you have any
questions regarding the applicability of
this action to a particular entity, consult
the person listed under FOR FURTHER
INFORMATION CONTACT.
B. How can I get electronic access to
other related information?
You may access a frequently updated
electronic version of 40 CFR part 180
through the Government Printing
Office’s e-CFR site at https://
ecfr.gpoaccess.gov/cgi/t/text/textidx?&c=ecfr&tpl=/ecfrbrowse/Title40/
40tab_02.tpl.
C. How can I file an objection or hearing
request?
Under FFDCA section 408(g), 21
U.S.C. 346a(g), any person may file an
objection to any aspect of this regulation
and may also request a hearing on those
objections. You must file your objection
or request a hearing on this regulation
in accordance with the instructions
provided in 40 CFR part 178. To ensure
proper receipt by EPA, you must
identify docket ID number EPA–HQ–
OPP–2009–0538 in the subject line on
the first page of your submission. All
objections and requests for a hearing
must be in writing, and must be
received by the Hearing Clerk on or
before December 27, 2011. Addresses for
mail and hand delivery of objections
and hearing requests are provided in 40
CFR 178.25(b).
In addition to filing an objection or
hearing request with the Hearing Clerk
as described in 40 CFR part 178, please
submit a copy of the filing that does not
contain any CBI for inclusion in the
public docket. Information not marked
confidential pursuant to 40 CFR part 2
may be disclosed publicly by EPA
without prior notice. Submit a copy of
your non-CBI objection or hearing
request, identified by docket ID number
EPA–HQOPP–2009–0538, by one of the
following methods:
• Federal eRulemaking Portal: https://
www.regulations.gov. Follow the on-line
instructions for submitting comments.
• Mail: OPP Regulatory Public Docket
(7502P), Environmental Protection
Agency, 1200 Pennsylvania Ave., NW.,
Washington, DC 20460–0001.
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• 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.
II. Background and Statutory Findings
In the Federal Register of September
23, 2009 (74 FR 48556) (FRL–8434–7),
EPA issued a notice pursuant to section
408(d)(3) of FFDCA, 21 U.S.C.
346a(d)(3), announcing the filing of a
pesticide tolerance petition (PP 9E7552)
by IR–4, Rutgers University, 500 College
Rd. East, Suite 201W, Princeton, NJ
08540 (on behalf of OmniLytics, Inc.,
9100 South 500 West, Sandy, UT
84070). The petition requested that 40
CFR part 180 be amended by
establishing an exemption from the
requirement of a tolerance for residues
of bacteriophage of Clavibacter
michiganensis subspecies
michiganensis. This notice referenced a
summary of the petition prepared by the
petitioner, IR–4, which is available in
the docket via https://
www.regulations.gov. There were no
comments received in response to the
notice of filing.
Section 408(c)(2)(A)(i) of FFDCA
allows EPA to establish an exemption
from the requirement for a tolerance (the
legal limit for a pesticide chemical
residue in or on a food) only if EPA
determines that the exemption is ‘‘safe.’’
Section 408(c)(2)(A)(ii) of FFDCA
defines ‘‘safe’’ to mean that ‘‘there is a
reasonable certainty that no harm will
result from aggregate exposure to the
pesticide chemical residue, including
all anticipated dietary exposures and all
other exposures for which there is
reliable information.’’ This includes
exposure through drinking water and in
residential settings but does not include
occupational exposure. Pursuant to
section 408(c)(2)(B) of FFDCA, in
establishing or maintaining in effect an
exemption from the requirement of a
tolerance, EPA must take into account
the factors set forth in section
408(b)(2)(C) of FFDCA, which require
EPA to give special consideration to
exposure of infants and children to the
pesticide chemical residue in
establishing a tolerance exemption and
to ‘‘ensure that there is a reasonable
certainty that no harm will result to
infants and children from aggregate
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exposure to the pesticide chemical
residue. * * *’’
Additionally, section 408(b)(2)(D) of
FFDCA requires that EPA consider
‘‘available information concerning the
cumulative effects of [a particular
pesticide’s] * * * residues and other
substances that have a common
mechanism of toxicity.’’
EPA performs a number of analyses to
determine the risks from aggregate
exposure to pesticide residues. First,
EPA determines the toxicity of
pesticides. Second, EPA examines
exposure to the pesticide through food,
drinking water, and through other
exposures that occur as a result of
pesticide use in residential settings.
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III. Toxicological Profile
Consistent with section 408(b)(2)(D)
of FFDCA, EPA has reviewed the
available scientific data and other
relevant information in support of this
action and considered its validity,
completeness, and reliability and the
relationship of this information to
human risk. EPA has also considered
available information concerning the
variability of the sensitivities of major
identifiable subgroups of consumers,
including infants and children.
A. Bacteriophage Overview
Bacteriophage, the most abundant
group of biological entities on the
planet, are naturally occurring viruses
that are found in soil and water and in
association with plants and animals,
including humans (Refs. 1 through 8).
Bacteriophage are obligate parasites of
bacteria, which means they attach to,
infect, and reproduce in bacteria, and
are host-specific for bacteria, with
specific bacteriophage attacking only
one bacterial species and most
frequently only one strain within a
bacterial species (Refs. 9 through 11). As
such, bacteriophage do not attack other
beneficial bacteria. In addition, there is
no evidence for bacteriophage infecting
any other life form, including humans,
except bacteria (Refs. 7, 12, and 13).
Humans and other animals commonly
consume bacteriophage as they are
abundantly found in water, on plant
surfaces, and in foods such as ground
beef, pork sausage, chicken, oysters,
cheese, mushrooms, and broccoli (Refs.
3, 4, and 14 through 19). In addition,
bacteriophage are common commensals
of the human gut and likely play an
important role in regulating populations
of various bacteria in the
gastrointestinal tract (Ref. 7). As cited in
public literature, bacteriophage have
been used for more than 80 years as
therapeutic agents with no ill effects
and are active against bacteria that cause
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many infections and human diseases
(Refs. 7, 20, and 21).
Since 2005, bacteriophage have also
been used in a pesticide product
(Agriphage; EPA Reg. No. 67986–1),
without reported incidents, to control
particular bacterial diseases
(Xanthomonas campestris pv.
vesicatoria and Pseduomonas syringae
pv. tomato) of tomato and pepper. In
conjunction with registration of the
aforementioned pesticide product, EPA
established an exemption from the
requirement of a tolerance for residues
of bacteriophage of Xanthomonas
campestris pv. vesicatoria and
´
Pseudomonas syringae pv. tomato in or
on tomato and pepper (see the Federal
Register of December 28, 2005 (70 FR
76704) (FRL–7753–6)). Much like the
previously registered bacteriophage,
OmniLytics, Inc. is proposing that
bacteriophage of Clavibacter
michiganensis subspecies
michiganensis be applied as a pesticide
for a very limited use-to control
bacterial canker disease on tomato.
B. Microbial Pesticide Toxicology Data
Requirements
All mammalian toxicology data
requirements supporting the request for
an exemption from the requirement of a
tolerance for residues of bacteriophage
of Clavibacter michiganensis subspecies
michiganensis in or on tomato have
been fulfilled with submission of valid
studies from the public literature (Refs.
22 and 23).
As mentioned in Unit III.A.,
bacteriophage are viruses that only
infect specific bacteria, a basic fact
supported by both information
presented in public literature and the
absence of reported adverse effects to
humans even with commonplace
exposure to bacteriophage. Literature
submitted established that
bacteriophage have been used
historically and through modern times
in lieu of or to assist the action of
antibiotics. Clinical uses encompass all
manner of administration from
injection/intravenous and surgical
wound applications to topical and
ingestible preparations. There have been
no reports of adverse effects from such
administrations and in other similar
cases using controlled scientific studies.
Also submitted were literature citations
showing that bacteriophage are common
and abundant in soils, are in a wide
range of plant materials, and are
generally present in high numbers in the
environment (e.g., up to 1010 plaqueforming units (PFU) per liter may be
found in non-polluted waters). Yet
again, no adverse effects to humans
have been reported with these types of
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66189
potential exposure. Moreover,
bacteriophage presence reported in
foods and feeds ranges from 101 to 105
PFU/100 grams (g) of meat and up to
107 PFU/100 g of cheese without any
known harmful effects after
consumption of such materials. Finally,
the petitioner noted that, during an
extensive history of bacteriophage
laboratory and pesticidal usage, adverse
reports in the literature have not been
documented and episodes of
hypersensitivity have not occurred.
Because bacteriophage are obligate
bacterial parasites and are not known to
infect humans, the only human health
risk associated with use of
bacteriophage of Clavibacter
michiganensis subspecies
michiganensis as a bactericide is
potential for acquisition and production
of microbial toxins. This acquisition
occurs through lysogeny, which is when
bacteriophage integrate into the genome
of toxigenic bacterial host strains and
pick up and transmit those genetic traits
to other bacteria that otherwise would
not produce toxic substances. Therefore,
bacteriophage of Clavibacter
michiganensis subspecies
michiganensis that meet the following
two conditions do not present this risk
issue:
1. Bacteriophage produced in
Clavibacter michiganensis subspecies
michiganensis, which has been
sequenced and determined to be an
atoxigenic host bacteria, and
2. Bacteriophage possessing the
capability to lyse host bacteria, i.e.,
completely destroy host cells during the
viral production process, which
precludes genetic transfer of possible
toxins to other bacteria (Ref. 22).
IV. Aggregate Exposure
In examining aggregate exposure,
section 408 of FFDCA directs EPA to
consider available information
concerning exposures from the pesticide
residue in food and all other nonoccupational exposures, including
drinking water from ground water or
surface water and exposure through
pesticide use in gardens, lawns, or
buildings (residential and other indoor
uses).
A. Dietary Exposure
1. Food exposure. Published literature
submitted by the petitioner, as well as
other publicly available literature,
indicate that bacteriophage are
commonly associated with food and are
therefore regularly consumed by
humans. According to Ackermann
(1997), these viruses have been found in
association with ‘‘buds, leaves, root
nodules (leguminous plants), roots,
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rotting fruit, seeds, stems, and straw;
crown gall tumors * * * healthy or
diseased alfalfa, barley, beans, broccoli,
Brussels sprouts, buckwheat, clover,
cotton, cucumber, lucerne, mulberry,
oats, peas, peach trees, radish, rutabaga,
ryegrass, rye, timothy, tobacco,
tomatoes, [and] wheat’’ (Ref. 14).
Moreover, bacteriophage have been
isolated from a wide range of food
products, including ground beef, pork
sausage, chicken, farmed freshwater
fish, common carp, marine fish, oil
sardines, raw skim milk, and cheese
(Refs. 15, 16, and 24 through 27). In fact,
several studies have suggested that
100% of the ground beef and chicken
meat sold at retail stores contain various
levels of bacteriophage. For instance,
bacteriophage were recovered from
100% of examined fresh chicken and
pork sausage samples and from 33% of
delicatessen meat samples analyzed; the
levels ranged from 3.3 × 1010 to 4.4 ×
1010 PFU/100 g of fresh chicken, up to
3.5 × 1010 PFU/100 g of fresh pork, and
up to 2.7 × 1010 PFU/100 g of roast
turkey breast samples (Ref 16). Other
studies similarly showed the
widespread occurrence of bacteriophage
in certain foods:
a. 38 bacteriophage-host systems were
isolated from 22 of 45 refrigerated
products (Ref 27);
b. Bacteriophage infecting fire blight
pathogen (Erwinia amylovora) were
isolated from apple, pear, and raspberry
tissues and from soil samples collected
at sites displaying fire blight symptoms
(Ref 5); and
c. Shellfish, which filter large
quantities of seawater, concentrated
both bacteria and bacteriophage (Ref 6).
Because lytic bacteriophage of
Clavibacter michiganensis subspecies
michiganensis produced in Clavibacter
michiganensis subspecies
michiganensis are intended to be
applied to tomatoes, it is likely that
dietary exposure will occur; however,
no adverse effects are expected to occur.
Despite constant and direct food
exposure to bacteriophage (examples
provided in the preceding paragraph
and in Unit III.), no adverse effects to
humans have been reported in publicly
available literature. Indeed, no such
effects are expected given that
bacteriophage, including the one at
issue in this action, are not capable of
infecting eukaryotic cells and are host
specific, attacking only bacteria.
2. Drinking water exposure. Published
literature submitted by the petitioner, as
well as other publicly available
literature, indicate that, much like food,
bacteriophage are commonly associated
with water and are therefore regularly
consumed by humans. According to
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Demuth et al. (1993), ‘‘Bacteriophage
* * * have been isolated from all types
of bacteria and from virtually any
aquatic or terrestrial habitat where
bacteria can exist. However, only in the
last few years has it been recognized
that viruses (phage) are extremely
abundant in ocean and fresh water and
may exceed the concentration of
bacteria by up to 100-fold’’ (Ref. 3).
Other studies showed that
bacteriophage of Erwinia carotovora and
Erwinia ananas were isolated from
certain freshwater lakes in Florida and
Texas (Ref. 4) and that coliphage were
present in some samples of drinking
water (Ref 28).
When lytic bacteriophage of
Clavibacter michiganensis subspecies
michiganensis produced in Clavibacter
michiganensis subspecies
michiganensis are applied to tomato as
a bactericide in accordance with good
agricultural practices, exposure of
humans to residues of these
bacteriophage in consumed drinking
water may occur. Although lytic
bacteriophage of Clavibacter
michiganensis subspecies
michiganensis produced in Clavibacter
michiganensis subspecies
michiganensis are not expected to reach
surface water because the proposed use
patterns do not include direct
application to aquatic sites, it is possible
that this microbial pest control agent
could make it into ground water.
Nonetheless, if oral exposure to lytic
bacteriophage of Clavibacter
michiganensis subspecies
michiganensis produced in Clavibacter
michiganensis subspecies
michiganensis occurs through
consumed drinking water (e.g., due to
surface water contamination by
microbial pesticide spray drift or runoff
or contact with ground water), for the
many reasons enumerated in Unit III.
and Unit IV.A.1., EPA concludes there
is reasonable certainty that this type of
drinking water exposure, or any level of
drinking water exposure for that matter,
will not result in harm to humans.
B. Other Non-Occupational Exposure
Dermal and inhalation nonoccupational exposures to lytic
bacteriophage of Clavibacter
michiganensis subspecies
michiganensis produced in Clavibacter
michiganensis subspecies
michiganensis are not expected as all
proposed pesticide applications will
take place in distinct agricultural
settings. Even if dermal and inhalation
non-occupational exposures were to
occur inadvertently (e.g., through spray
drift) or due to an eventual expansion of
use sites, such exposures would not be
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of concern given the information
presented in Unit III. and Unit IV.A.
V. Cumulative Effects From Substances
With a Common Mechanism of Toxicity
Section 408(b)(2)(D)(v) of FFDCA
requires that, when considering whether
to establish, modify, or revoke a
tolerance exemption, EPA consider
‘‘available information concerning the
cumulative effects of [a particular
pesticide’s] * * * residues and other
substances that have a common
mechanism of toxicity.’’
EPA has not found lytic bacteriophage
of Clavibacter michiganensis subspecies
michiganensis produced in Clavibacter
michiganensis subspecies
michiganensis to share a common
mechanism of toxicity with any other
substances, and lytic bacteriophage of
Clavibacter michiganensis subspecies
michiganensis produced in Clavibacter
michiganensis subspecies
michiganensis do not appear to produce
a toxic metabolite against the target pest.
For the purposes of this tolerance
action, therefore, EPA has assumed that
lytic bacteriophage of Clavibacter
michiganensis subspecies
michiganensis produced in Clavibacter
michiganensis subspecies
michiganensis do not have a common
mechanism of toxicity with other
substances. Therefore, section
408(b)(2)(D)(v) of the FFDCA does not
apply. For information regarding EPA’s
efforts to determine which chemicals
have a common mechanism of toxicity
and to evaluate the cumulative effects of
such chemicals, see EPA’s Web site at
https://www.epa.gov/pesticides/
cumulative.
VI. Determination of Safety for United
States (U.S.) Population, Infants and
Children
FFDCA section 408(b)(2)(C) provides
that EPA shall assess the available
information about consumption patterns
among infants and children, special
susceptibility of infants and children to
pesticide chemical residues, and the
cumulative effects on infants and
children of the residues and other
substances with a common mechanism
of toxicity. In addition, FFDCA section
408(b)(2)(C) provides that EPA shall
apply an additional tenfold (10×) margin
of safety for infants and children in the
case of threshold effects to account for
prenatal and postnatal toxicity and the
completeness of the database on toxicity
and exposure unless EPA determines
that a different margin of safety will be
safe for infants and children. This
additional margin of safety is commonly
referred to as the Food Quality
Protection Act Safety Factor. In
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applying this provision, EPA either
retains the default value of 10× or uses
a different additional safety factor when
reliable data available to EPA support
the choice of a different factor.
As previously discussed in Unit III.
and Unit IV., humans, including infants
and children, have been exposed to
bacteriophage through food and water,
where they are commonly found, and
through decades of therapeutic use with
no known or reported adverse effects.
Based on this, as well as all the other
reasons enumerated repeatedly in this
unit, EPA concludes that there is a
reasonable certainty that no harm will
result to the U.S. population, including
infants and children, from aggregate
exposure to the residues of lytic
bacteriophage of Clavibacter
michiganensis subspecies
michiganensis produced in Clavibacter
michiganensis subspecies
michiganensis. Such exposure includes
all anticipated dietary exposures and all
other exposures for which there is
reliable information. EPA has arrived at
this conclusion because, considered
collectively, the public literature
available on bacteriophage, including
the one at issue in this action, do not
demonstrate toxic, pathogenic, and/or
infective potential to mammals. Thus,
there are no threshold effects of concern
and, as a result, an additional margin of
safety is not necessary.
VII. Other Considerations
A. Analytical Enforcement Methodology
An analytical method is not required
for enforcement purposes for the
reasons stated above and because EPA is
establishing an exemption from the
requirement of a tolerance without any
numerical limitation.
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B. International Residue Limits
In making its tolerance decisions, EPA
seeks to harmonize U.S. tolerances with
international standards whenever
possible, consistent with U.S. food
safety standards and agricultural
practices. In this context, EPA considers
the international maximum residue
limits (MRLs) established by the Codex
Alimentarius Commission (Codex), as
required by FFDCA section 408(b)(4).
The Codex Alimentarius is a joint U.N.
Food and Agriculture Organization/
World Health Organization food
standards program, and it is recognized
as an international food safety
standards-setting organization in trade
agreements to which the United States
is a party. EPA may establish a tolerance
that is different from a Codex MRL;
however, FFDCA section 408(b)(4)
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requires that EPA explain the reasons
for departing from the Codex level.
The Codex has not established a MRL
for lytic bacteriophage of Clavibacter
michiganensis subspecies
michiganensis produced in Clavibacter
michiganensis subspecies
michiganensis.
C. Revisions to Requested Exemption
In its petition, the petitioner
requested generally that the Agency
issue an exemption from the
requirement of a tolerance for residues
of bacteriophage of Clavibacter
michiganensis subspecies
michiganensis in or on tomato. The
petitioner’s supporting materials
indicated that the actual pesticide that
would be used would be safe because
the bacteriophage were lytic and
produced in Clavibacter michiganensis
subspecies michiganensis. The Agency
believes both that these two conditions
are necessary to make the safety finding
and the petitioner was only requesting
a narrow exemption; therefore, the
Agency is modifying the tolerance
exemption regulatory text to include
such criteria.
VIII. Conclusions
EPA concludes that there is a
reasonable certainty that no harm will
result to the U.S. population, including
infants and children, from aggregate
exposure to residues of lytic
bacteriophage of Clavibacter
michiganensis subspecies
michiganensis produced in Clavibacter
michiganensis subspecies
michiganensis. Therefore, an exemption
from the requirement of a tolerance is
established for residues of lytic
bacteriophage of Clavibacter
michiganensis subspecies
michiganensis produced in Clavibacter
michiganensis subspecies
michiganensis in or on tomato when
applied as a bactericide in accordance
with good agricultural practices.
IX. References
1. Keel C, Ucurum Z, Michaux P, Adrian M,
Haas D. 2002. Deleterious impact of a
virulent bacteriophage on survival and
biocontrol activity of Pseudomonas
fluorescens strain CHAO in natural soil.
Molecular Plant-Microbe Interactions
15:567–576.
2. Liew KW, Alvarez AM. 1981. Biological
and morphological characterization of
Xanthomonas campestris bacteriophages.
Phytopatholoy 71:269–273.
3. Demuth J, Neve H, Witzel K–P. 1993.
Direct electron microscopy study on the
morphological diversity of bacteriophage
populations in Lake Plussse. Applied
and Environmental Microbiology
59:3378–3384.
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66191
4. Eayre CG, Bartz JA, Concelmo DE. 1995.
Bacteriophages of Erwinia carotovora
and Erwinia ananas isolated from
freshwater lakes. Plant Disease 79:801–
804.
5. Schnabel EL, Jones AL. 2001. Isolation and
characterization of five Erwinia
amylovora bacteriophages and
assessment of phage resistance in strains
of Erwinia amylovora. Applied and
Environmental Microbiology 67:59–64.
6. Denis FA. 1975. Contamination of shellfish
with strains of Pseudomonas aeruginosa
and specific bacteriophages. Canadian
Journal of Microbiology 21:1055–1057.
7. Merril CR, Scholl D, Adhya SL. 2003. The
prospect for bacteriophage therapy in
Western medicine. Nature 2:489–497.
8. Rohwer F. 2003. Global phage diversity.
Cell 113:1–2.
9. Stocker BAD. 1955. Bacteriophage and
bacterial classification. Journal of
General Microbiology 12:375–381.
10. Duckworth DH, Gulig PA. 2002.
Bacteriophage: potential treatment for
bacterial infections. Biodrugs 16:57–62.
11. Summers WC. 2001. Bacteriophage
therapy. Annual Review of Microbiology
55:437–451.
12. Lorch A. 1999. Bacteriophage: an
alternative to antibiotics? Biotechnology
and Development Monitor 39:14–17.
13. Petricciani JC, Hsu TC, Stock AD, Turner
JH, Wenger SL, Elisberg BL. 1978.
Bacteriophages, vaccines, and people: an
assessment of risk. Proceedings of the
Society for Experimental Biology and
Medicine. 58:378–382.
14. Ackermann H–W. 1997. Bacteriophage
ecology. Pp. 335–339 in: ‘‘Progress in
Microbial Ecology (Proceedings of
Seventh International Symposium on
Microbial Ecology)’’. Martins MT, Sato
¨
MIZ, Tiedje JM, Hagler LCN, Dobereiner
J, Sanchez PS, eds. Brazilian Society for
Microbiology.
15. Kennedy JE Jr, Wei CI, Oblinger JL. 1986.
Methodology for enumeration of
coliphages in foods. Applied and
Environmental Microbiology 51:956–962.
16. Kennedy JE Jr, Oblinger JL, Bitton G.
1984. Recovery of coliphages from
chicken, pork sausage and delicatessen
meats. Journal of Food Protection
47:623–626.
17. DePaola A, Motes ML, Chan AM, Suttle
CA. 1998. Phages infecting Vibrio
vulnificus are abundant and diverse in
oysters (Crassostrea virginica) collected
from the Gulf of Mexico. Applied and
Environmental Microbiology 64:346–351.
18. Quiberoni A, Tremblay D, Ackermann H–
W, Moineau S, Reinheimer JA. 2006.
Diversity of Streptococcus thermophilus
phages in a large-production cheese
factory in Argentina. Journal of Dairy
Science 89:3791–3799.
19. Guillaumes J, Houdeau G, Germain R,
Olivier JM. 1988. Improvement of the
biocontrol of Pseudomonas tolaasii using
bacteriophages associated with an
antagonistic bacterium. Bulletin OEPP
18:77–82.
20. Radetsky P. 1996. The good virus.
Discover 17:50–58.
21. Chanishvili N, Chanishvili T, Tediashvili
M, Barrow PA. 2001. Phages and their
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application against drug-resistant
bacteria. Journal of Chemical Technology
and Biotechnology 76:689–699.
22. U.S. EPA. 2011. Bacteriophage of
Clavibacter michiganensis subsp.
michiganensis—AgriPhage CMM.
Memorandum from J.V. Gagliardi, Ph.D.
to A. Gross dated June 30, 2011.
23. U.S. EPA. 2011. Bacteriophage of
Clavibacter michiganensis subspecies
michiganensis Biopesticides Registration
Action Document dated August 25, 2011
(available as ‘‘Supporting & Related
Material’’ with docket ID number EPA–
HQ–OPP2009–0539 at https://www.
regulations.gov).
24. Atterbury RJ, Connerton PL, Dodd CER,
Rees CED, Connerton IF. 2003. Isolation
and characterization of Campylobacter
bacteriophages from retail poultry.
Applied and Environmental
Microbiology 69:4511–4518.
25. Gautier M, Rouault A, Sommer P,
Briandet R. 1995. Occurrence of
Propionibacterium freudenreichii
bacteriophages in swiss cheese. Applied
and Environmental Microbiology
61:2572–2576.
26. Greer GG. 2005. Bacteriophage control of
foodborne bacteria. Journal of Food
Protection 68:1102–1111.
27. Whitman PA, Marshall RT. 1971.
Isolation of psychrophilic
bacteriophagehost systems from
refrigerated food products. Applied
Microbiology 22:220–223.
28. El-Abagy MM, Dutka BJ, Kamel M. 1988.
Incidence of coliphage in potable water
supplies. Applied and Environmental
Microbiology 54:1632–1633.
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X. Statutory and Executive Order
Reviews
This final rule establishes a tolerance
exemption under section 408(d) of
FFDCA in response to a petition
submitted to EPA. The Office of
Management and Budget (OMB) has
exempted these types of actions from
review under Executive Order 12866,
entitled Regulatory Planning and
Review (58 FR 51735, October 4, 1993).
Because this final rule has been
exempted from review under Executive
Order 12866, this final rule is not
subject to Executive Order 13211,
entitled Actions Concerning Regulations
That Significantly Affect Energy Supply,
Distribution, or Use (66 FR 28355, May
22, 2001), or Executive Order 13045,
entitled Protection of Children from
Environmental Health Risks and Safety
Risks (62 FR 19885, April 23, 1997).
This final rule does not contain any
information collections subject to OMB
approval under the Paperwork
Reduction Act (PRA), 44 U.S.C. 3501 et
seq., nor does it require any special
considerations under Executive Order
12898, entitled Federal Actions to
Address Environmental Justice in
Minority Populations and Low-Income
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15:10 Oct 25, 2011
Jkt 226001
Populations (59 FR 7629, February 16,
1994).
Since tolerances and exemptions that
are established on the basis of a petition
under section 408(d) of FFDCA, such as
the tolerance exemption in this final
rule, do not require the issuance of a
proposed rule, the requirements of the
Regulatory Flexibility Act (RFA) (5
U.S.C. 601 et seq.) do not apply.
This final rule directly regulates
growers, food processors, food handlers,
and food retailers, not States or tribes.
As a result, this action does not alter the
relationships or distribution of power
and responsibilities established by
Congress in the preemption provisions
of section 408(n)(4) of FFDCA. As such,
EPA has determined that this action will
not have a substantial direct effect on
States or tribal governments, on the
relationship between the national
government and the States or tribal
governments, or on the distribution of
power and responsibilities among the
various levels of government or between
the Federal Government and Indian
tribes. Thus, EPA has determined that
Executive Order 13132, entitled
Federalism (64 FR 43255, August 10,
1999), and Executive Order 13175,
entitled Consultation and Coordination
with Indian Tribal Governments (65 FR
67249, November 9, 2000), do not apply
to this final rule. In addition, this final
rule does not impose any enforceable
duty or contain any unfunded mandate
as described under Title II of the
Unfunded Mandates Reform Act of 1995
(UMRA) (Pub. L. 104–4).
This action does not involve any
technical standards that would require
EPA consideration of voluntary
consensus standards pursuant to section
12(d) of the National Technology
Transfer and Advancement Act of 1995
(NTTAA), Public Law 104–113, section
12(d) (15 U.S.C. 272 note).
XI. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report to each House of
the Congress and to the Comptroller
General of the United States. EPA will
submit a report containing this rule and
other required information to the U.S.
Senate, the U.S. House of
Representatives, and the Comptroller
General of the United States prior to
publication of this final rule in the
Federal Register. This final rule is not
a ‘‘major rule’’ as defined by 5 U.S.C.
804(2).
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List of Subjects in 40 CFR Part 180
Environmental protection,
Administrative practice and procedure,
Agricultural commodities, Pesticides
and pests, Reporting and recordkeeping
requirements.
Dated: September 30, 2011.
Steven Bradbury,
Director, Office of Pesticide Programs.
Therefore, 40 CFR chapter I is
amended as follows:
PART 180—[AMENDED]
1. The authority citation for part 180
continues to read as follows:
■
Authority: 21 U.S.C. 321(q), 346a and 371.
2. Section 180.1307 is added to
subpart D to read as follows:
■
§ 180.1307 Bacteriophage of Clavibacter
michiganensis subspecies michiganensis;
exemption from the requirement of a
tolerance.
An exemption from the requirement
of a tolerance is established for residues
of lytic bacteriophage of Clavibacter
michiganensis subspecies
michiganensis produced in Clavibacter
michiganensis subspecies
michiganensis in or on tomato when
applied as a bactericide in accordance
with good agricultural practices.
[FR Doc. 2011–27042 Filed 10–25–11; 8:45 am]
BILLING CODE 6560–50–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 648
[Docket No. 101119575–1554–02]
RIN 0648–BA46
Fisheries of the Northeastern United
States; Monkfish; Framework
Adjustment 7
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
AGENCY:
This final rule implements
measures that were approved in
Framework Adjustment 7 to the
Monkfish Fishery Management Plan.
The New England Fishery Management
Council and Mid-Atlantic Fishery
Management Council developed
Framework Adjustment 7 to adjust the
annual catch target for the Northern
Fishery Management Area to be
consistent with the most recent
SUMMARY:
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Agencies
[Federal Register Volume 76, Number 207 (Wednesday, October 26, 2011)]
[Rules and Regulations]
[Pages 66187-66192]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2011-27042]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 180
[EPA-HQ-OPP-2009-0538; FRL-8891-3]
Bacteriophage of Clavibacter Michiganensis Subspecies
Michiganensis; Exemption From the Requirement of a Tolerance
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This regulation establishes an exemption from the requirement
of a tolerance for residues of lytic bacteriophage of Clavibacter
michiganensis subspecies michiganensis produced in Clavibacter
michiganensis subspecies michiganensis in or on tomato when applied as
a bactericide in accordance with good agricultural practices. On behalf
of OmniLytics, Inc., Interregional Research Project Number 4 (IR-4)
submitted a petition to EPA under the Federal Food, Drug, and Cosmetic
Act (FFDCA) requesting an exemption from
[[Page 66188]]
the requirement of a tolerance. This regulation eliminates the need to
establish a maximum permissible level for residues of lytic
bacteriophage of Clavibacter michiganensis subspecies michiganensis
produced in Clavibacter michiganensis subspecies michiganensis under
the FFDCA.
DATES: This regulation is effective October 26, 2011. Objections and
requests for hearings must be received on or before December 27, 2011,
and must be filed in accordance with the instructions provided in 40
CFR part 178 (see also Unit I.C. of the SUPPLEMENTARY INFORMATION).
ADDRESSES: EPA has established a docket for this action under docket
identification (ID) number EPA-HQ-OPP-2009-0538. 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., Confidential Business Information (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 in the electronic
docket at https://www.regulations.gov, or, if only available in hard
copy, at the Office of Pesticide Programs (OPP) Regulatory Public
Docket in Rm. S-4400, One Potomac Yard (South Bldg.), 2777 S. Crystal
Dr., Arlington, VA. The Docket Facility is open 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: Denise Greenway, Biopesticides and
Pollution Prevention Division (7511P), Office of Pesticide Programs,
Environmental Protection Agency, 1200 Pennsylvania Ave., NW.,
Washington, DC 20460-0001; telephone number: (703) 308-8263; e-mail
address: greenway.denise@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this action apply to me?
You may be potentially affected by this action if you are an
agricultural producer, food manufacturer, or pesticide manufacturer.
Potentially affected entities may include, but are not limited to:
Crop production (NAICS code 111).
Animal production (NAICS code 112).
Food manufacturing (NAICS code 311).
Pesticide manufacturing (NAICS code 32532).
This listing is not intended to be exhaustive, but rather provides
a guide for readers regarding entities likely to be affected by this
action. Other types of entities not listed in this unit could also be
affected. The North American Industrial Classification System (NAICS)
codes have been provided to assist you and others in determining
whether this action might apply to certain entities. If you have any
questions regarding the applicability of this action to a particular
entity, consult the person listed under FOR FURTHER INFORMATION
CONTACT.
B. How can I get electronic access to other related information?
You may access a frequently updated electronic version of 40 CFR
part 180 through the Government Printing Office's e-CFR site at https://ecfr.gpoaccess.gov/cgi/t/text/text-idx?&c=ecfr&tpl=/ecfrbrowse/Title40/40tab_02.tpl.
C. How can I file an objection or hearing request?
Under FFDCA section 408(g), 21 U.S.C. 346a(g), any person may file
an objection to any aspect of this regulation and may also request a
hearing on those objections. You must file your objection or request a
hearing on this regulation in accordance with the instructions provided
in 40 CFR part 178. To ensure proper receipt by EPA, you must identify
docket ID number EPA-HQ-OPP-2009-0538 in the subject line on the first
page of your submission. All objections and requests for a hearing must
be in writing, and must be received by the Hearing Clerk on or before
December 27, 2011. Addresses for mail and hand delivery of objections
and hearing requests are provided in 40 CFR 178.25(b).
In addition to filing an objection or hearing request with the
Hearing Clerk as described in 40 CFR part 178, please submit a copy of
the filing that does not contain any CBI for inclusion in the public
docket. Information not marked confidential pursuant to 40 CFR part 2
may be disclosed publicly by EPA without prior notice. Submit a copy of
your non-CBI objection or hearing request, identified by docket ID
number EPA-HQOPP-2009-0538, by one of the following methods:
Federal eRulemaking Portal: https://www.regulations.gov.
Follow the on-line instructions for submitting comments.
Mail: 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.
II. Background and Statutory Findings
In the Federal Register of September 23, 2009 (74 FR 48556) (FRL-
8434-7), EPA issued a notice pursuant to section 408(d)(3) of FFDCA, 21
U.S.C. 346a(d)(3), announcing the filing of a pesticide tolerance
petition (PP 9E7552) by IR-4, Rutgers University, 500 College Rd. East,
Suite 201W, Princeton, NJ 08540 (on behalf of OmniLytics, Inc., 9100
South 500 West, Sandy, UT 84070). The petition requested that 40 CFR
part 180 be amended by establishing an exemption from the requirement
of a tolerance for residues of bacteriophage of Clavibacter
michiganensis subspecies michiganensis. This notice referenced a
summary of the petition prepared by the petitioner, IR-4, which is
available in the docket via https://www.regulations.gov. There were no
comments received in response to the notice of filing.
Section 408(c)(2)(A)(i) of FFDCA allows EPA to establish an
exemption from the requirement for a tolerance (the legal limit for a
pesticide chemical residue in or on a food) only if EPA determines that
the exemption is ``safe.'' Section 408(c)(2)(A)(ii) of FFDCA defines
``safe'' to mean that ``there is a reasonable certainty that no harm
will result from aggregate exposure to the pesticide chemical residue,
including all anticipated dietary exposures and all other exposures for
which there is reliable information.'' This includes exposure through
drinking water and in residential settings but does not include
occupational exposure. Pursuant to section 408(c)(2)(B) of FFDCA, in
establishing or maintaining in effect an exemption from the requirement
of a tolerance, EPA must take into account the factors set forth in
section 408(b)(2)(C) of FFDCA, which require EPA to give special
consideration to exposure of infants and children to the pesticide
chemical residue in establishing a tolerance exemption and to ``ensure
that there is a reasonable certainty that no harm will result to
infants and children from aggregate
[[Page 66189]]
exposure to the pesticide chemical residue. * * *''
Additionally, section 408(b)(2)(D) of FFDCA requires that EPA
consider ``available information concerning the cumulative effects of
[a particular pesticide's] * * * residues and other substances that
have a common mechanism of toxicity.''
EPA performs a number of analyses to determine the risks from
aggregate exposure to pesticide residues. First, EPA determines the
toxicity of pesticides. Second, EPA examines exposure to the pesticide
through food, drinking water, and through other exposures that occur as
a result of pesticide use in residential settings.
III. Toxicological Profile
Consistent with section 408(b)(2)(D) of FFDCA, EPA has reviewed the
available scientific data and other relevant information in support of
this action and considered its validity, completeness, and reliability
and the relationship of this information to human risk. EPA has also
considered available information concerning the variability of the
sensitivities of major identifiable subgroups of consumers, including
infants and children.
A. Bacteriophage Overview
Bacteriophage, the most abundant group of biological entities on
the planet, are naturally occurring viruses that are found in soil and
water and in association with plants and animals, including humans
(Refs. 1 through 8). Bacteriophage are obligate parasites of bacteria,
which means they attach to, infect, and reproduce in bacteria, and are
host-specific for bacteria, with specific bacteriophage attacking only
one bacterial species and most frequently only one strain within a
bacterial species (Refs. 9 through 11). As such, bacteriophage do not
attack other beneficial bacteria. In addition, there is no evidence for
bacteriophage infecting any other life form, including humans, except
bacteria (Refs. 7, 12, and 13). Humans and other animals commonly
consume bacteriophage as they are abundantly found in water, on plant
surfaces, and in foods such as ground beef, pork sausage, chicken,
oysters, cheese, mushrooms, and broccoli (Refs. 3, 4, and 14 through
19). In addition, bacteriophage are common commensals of the human gut
and likely play an important role in regulating populations of various
bacteria in the gastrointestinal tract (Ref. 7). As cited in public
literature, bacteriophage have been used for more than 80 years as
therapeutic agents with no ill effects and are active against bacteria
that cause many infections and human diseases (Refs. 7, 20, and 21).
Since 2005, bacteriophage have also been used in a pesticide
product (Agriphage; EPA Reg. No. 67986-1), without reported incidents,
to control particular bacterial diseases (Xanthomonas campestris pv.
vesicatoria and Pseduomonas syringae pv. tomato) of tomato and pepper.
In conjunction with registration of the aforementioned pesticide
product, EPA established an exemption from the requirement of a
tolerance for residues of bacteriophage of Xanthomonas campestris pv.
vesicatoria and Pseud[oacute]monas syringae pv. tomato in or on tomato
and pepper (see the Federal Register of December 28, 2005 (70 FR 76704)
(FRL-7753-6)). Much like the previously registered bacteriophage,
OmniLytics, Inc. is proposing that bacteriophage of Clavibacter
michiganensis subspecies michiganensis be applied as a pesticide for a
very limited use-to control bacterial canker disease on tomato.
B. Microbial Pesticide Toxicology Data Requirements
All mammalian toxicology data requirements supporting the request
for an exemption from the requirement of a tolerance for residues of
bacteriophage of Clavibacter michiganensis subspecies michiganensis in
or on tomato have been fulfilled with submission of valid studies from
the public literature (Refs. 22 and 23).
As mentioned in Unit III.A., bacteriophage are viruses that only
infect specific bacteria, a basic fact supported by both information
presented in public literature and the absence of reported adverse
effects to humans even with commonplace exposure to bacteriophage.
Literature submitted established that bacteriophage have been used
historically and through modern times in lieu of or to assist the
action of antibiotics. Clinical uses encompass all manner of
administration from injection/intravenous and surgical wound
applications to topical and ingestible preparations. There have been no
reports of adverse effects from such administrations and in other
similar cases using controlled scientific studies. Also submitted were
literature citations showing that bacteriophage are common and abundant
in soils, are in a wide range of plant materials, and are generally
present in high numbers in the environment (e.g., up to 1010 plaque-
forming units (PFU) per liter may be found in non-polluted waters). Yet
again, no adverse effects to humans have been reported with these types
of potential exposure. Moreover, bacteriophage presence reported in
foods and feeds ranges from 101 to 105 PFU/100 grams (g) of meat and up
to 107 PFU/100 g of cheese without any known harmful effects after
consumption of such materials. Finally, the petitioner noted that,
during an extensive history of bacteriophage laboratory and pesticidal
usage, adverse reports in the literature have not been documented and
episodes of hypersensitivity have not occurred.
Because bacteriophage are obligate bacterial parasites and are not
known to infect humans, the only human health risk associated with use
of bacteriophage of Clavibacter michiganensis subspecies michiganensis
as a bactericide is potential for acquisition and production of
microbial toxins. This acquisition occurs through lysogeny, which is
when bacteriophage integrate into the genome of toxigenic bacterial
host strains and pick up and transmit those genetic traits to other
bacteria that otherwise would not produce toxic substances. Therefore,
bacteriophage of Clavibacter michiganensis subspecies michiganensis
that meet the following two conditions do not present this risk issue:
1. Bacteriophage produced in Clavibacter michiganensis subspecies
michiganensis, which has been sequenced and determined to be an
atoxigenic host bacteria, and
2. Bacteriophage possessing the capability to lyse host bacteria,
i.e., completely destroy host cells during the viral production
process, which precludes genetic transfer of possible toxins to other
bacteria (Ref. 22).
IV. Aggregate Exposure
In examining aggregate exposure, section 408 of FFDCA directs EPA
to consider available information concerning exposures from the
pesticide residue in food and all other non-occupational exposures,
including drinking water from ground water or surface water and
exposure through pesticide use in gardens, lawns, or buildings
(residential and other indoor uses).
A. Dietary Exposure
1. Food exposure. Published literature submitted by the petitioner,
as well as other publicly available literature, indicate that
bacteriophage are commonly associated with food and are therefore
regularly consumed by humans. According to Ackermann (1997), these
viruses have been found in association with ``buds, leaves, root
nodules (leguminous plants), roots,
[[Page 66190]]
rotting fruit, seeds, stems, and straw; crown gall tumors * * * healthy
or diseased alfalfa, barley, beans, broccoli, Brussels sprouts,
buckwheat, clover, cotton, cucumber, lucerne, mulberry, oats, peas,
peach trees, radish, rutabaga, ryegrass, rye, timothy, tobacco,
tomatoes, [and] wheat'' (Ref. 14). Moreover, bacteriophage have been
isolated from a wide range of food products, including ground beef,
pork sausage, chicken, farmed freshwater fish, common carp, marine
fish, oil sardines, raw skim milk, and cheese (Refs. 15, 16, and 24
through 27). In fact, several studies have suggested that 100% of the
ground beef and chicken meat sold at retail stores contain various
levels of bacteriophage. For instance, bacteriophage were recovered
from 100% of examined fresh chicken and pork sausage samples and from
33% of delicatessen meat samples analyzed; the levels ranged from 3.3 x
1010 to 4.4 x 1010 PFU/100 g of fresh chicken, up to 3.5 x 1010 PFU/100
g of fresh pork, and up to 2.7 x 1010 PFU/100 g of roast turkey breast
samples (Ref 16). Other studies similarly showed the widespread
occurrence of bacteriophage in certain foods:
a. 38 bacteriophage-host systems were isolated from 22 of 45
refrigerated products (Ref 27);
b. Bacteriophage infecting fire blight pathogen (Erwinia amylovora)
were isolated from apple, pear, and raspberry tissues and from soil
samples collected at sites displaying fire blight symptoms (Ref 5); and
c. Shellfish, which filter large quantities of seawater,
concentrated both bacteria and bacteriophage (Ref 6).
Because lytic bacteriophage of Clavibacter michiganensis subspecies
michiganensis produced in Clavibacter michiganensis subspecies
michiganensis are intended to be applied to tomatoes, it is likely that
dietary exposure will occur; however, no adverse effects are expected
to occur. Despite constant and direct food exposure to bacteriophage
(examples provided in the preceding paragraph and in Unit III.), no
adverse effects to humans have been reported in publicly available
literature. Indeed, no such effects are expected given that
bacteriophage, including the one at issue in this action, are not
capable of infecting eukaryotic cells and are host specific, attacking
only bacteria.
2. Drinking water exposure. Published literature submitted by the
petitioner, as well as other publicly available literature, indicate
that, much like food, bacteriophage are commonly associated with water
and are therefore regularly consumed by humans. According to Demuth et
al. (1993), ``Bacteriophage * * * have been isolated from all types of
bacteria and from virtually any aquatic or terrestrial habitat where
bacteria can exist. However, only in the last few years has it been
recognized that viruses (phage) are extremely abundant in ocean and
fresh water and may exceed the concentration of bacteria by up to 100-
fold'' (Ref. 3). Other studies showed that bacteriophage of Erwinia
carotovora and Erwinia ananas were isolated from certain freshwater
lakes in Florida and Texas (Ref. 4) and that coliphage were present in
some samples of drinking water (Ref 28).
When lytic bacteriophage of Clavibacter michiganensis subspecies
michiganensis produced in Clavibacter michiganensis subspecies
michiganensis are applied to tomato as a bactericide in accordance with
good agricultural practices, exposure of humans to residues of these
bacteriophage in consumed drinking water may occur. Although lytic
bacteriophage of Clavibacter michiganensis subspecies michiganensis
produced in Clavibacter michiganensis subspecies michiganensis are not
expected to reach surface water because the proposed use patterns do
not include direct application to aquatic sites, it is possible that
this microbial pest control agent could make it into ground water.
Nonetheless, if oral exposure to lytic bacteriophage of Clavibacter
michiganensis subspecies michiganensis produced in Clavibacter
michiganensis subspecies michiganensis occurs through consumed drinking
water (e.g., due to surface water contamination by microbial pesticide
spray drift or runoff or contact with ground water), for the many
reasons enumerated in Unit III. and Unit IV.A.1., EPA concludes there
is reasonable certainty that this type of drinking water exposure, or
any level of drinking water exposure for that matter, will not result
in harm to humans.
B. Other Non-Occupational Exposure
Dermal and inhalation non-occupational exposures to lytic
bacteriophage of Clavibacter michiganensis subspecies michiganensis
produced in Clavibacter michiganensis subspecies michiganensis are not
expected as all proposed pesticide applications will take place in
distinct agricultural settings. Even if dermal and inhalation non-
occupational exposures were to occur inadvertently (e.g., through spray
drift) or due to an eventual expansion of use sites, such exposures
would not be of concern given the information presented in Unit III.
and Unit IV.A.
V. Cumulative Effects From Substances With a Common Mechanism of
Toxicity
Section 408(b)(2)(D)(v) of FFDCA requires that, when considering
whether to establish, modify, or revoke a tolerance exemption, EPA
consider ``available information concerning the cumulative effects of
[a particular pesticide's] * * * residues and other substances that
have a common mechanism of toxicity.''
EPA has not found lytic bacteriophage of Clavibacter michiganensis
subspecies michiganensis produced in Clavibacter michiganensis
subspecies michiganensis to share a common mechanism of toxicity with
any other substances, and lytic bacteriophage of Clavibacter
michiganensis subspecies michiganensis produced in Clavibacter
michiganensis subspecies michiganensis do not appear to produce a toxic
metabolite against the target pest. For the purposes of this tolerance
action, therefore, EPA has assumed that lytic bacteriophage of
Clavibacter michiganensis subspecies michiganensis produced in
Clavibacter michiganensis subspecies michiganensis do not have a common
mechanism of toxicity with other substances. Therefore, section
408(b)(2)(D)(v) of the FFDCA does not apply. For information regarding
EPA's efforts to determine which chemicals have a common mechanism of
toxicity and to evaluate the cumulative effects of such chemicals, see
EPA's Web site at https://www.epa.gov/pesticides/cumulative.
VI. Determination of Safety for United States (U.S.) Population,
Infants and Children
FFDCA section 408(b)(2)(C) provides that EPA shall assess the
available information about consumption patterns among infants and
children, special susceptibility of infants and children to pesticide
chemical residues, and the cumulative effects on infants and children
of the residues and other substances with a common mechanism of
toxicity. In addition, FFDCA section 408(b)(2)(C) provides that EPA
shall apply an additional tenfold (10x) margin of safety for infants
and children in the case of threshold effects to account for prenatal
and postnatal toxicity and the completeness of the database on toxicity
and exposure unless EPA determines that a different margin of safety
will be safe for infants and children. This additional margin of safety
is commonly referred to as the Food Quality Protection Act Safety
Factor. In
[[Page 66191]]
applying this provision, EPA either retains the default value of 10x or
uses a different additional safety factor when reliable data available
to EPA support the choice of a different factor.
As previously discussed in Unit III. and Unit IV., humans,
including infants and children, have been exposed to bacteriophage
through food and water, where they are commonly found, and through
decades of therapeutic use with no known or reported adverse effects.
Based on this, as well as all the other reasons enumerated repeatedly
in this unit, EPA concludes that there is a reasonable certainty that
no harm will result to the U.S. population, including infants and
children, from aggregate exposure to the residues of lytic
bacteriophage of Clavibacter michiganensis subspecies michiganensis
produced in Clavibacter michiganensis subspecies michiganensis. Such
exposure includes all anticipated dietary exposures and all other
exposures for which there is reliable information. EPA has arrived at
this conclusion because, considered collectively, the public literature
available on bacteriophage, including the one at issue in this action,
do not demonstrate toxic, pathogenic, and/or infective potential to
mammals. Thus, there are no threshold effects of concern and, as a
result, an additional margin of safety is not necessary.
VII. Other Considerations
A. Analytical Enforcement Methodology
An analytical method is not required for enforcement purposes for
the reasons stated above and because EPA is establishing an exemption
from the requirement of a tolerance without any numerical limitation.
B. International Residue Limits
In making its tolerance decisions, EPA seeks to harmonize U.S.
tolerances with international standards whenever possible, consistent
with U.S. food safety standards and agricultural practices. In this
context, EPA considers the international maximum residue limits (MRLs)
established by the Codex Alimentarius Commission (Codex), as required
by FFDCA section 408(b)(4). The Codex Alimentarius is a joint U.N. Food
and Agriculture Organization/World Health Organization food standards
program, and it is recognized as an international food safety
standards-setting organization in trade agreements to which the United
States is a party. EPA may establish a tolerance that is different from
a Codex MRL; however, FFDCA section 408(b)(4) requires that EPA explain
the reasons for departing from the Codex level.
The Codex has not established a MRL for lytic bacteriophage of
Clavibacter michiganensis subspecies michiganensis produced in
Clavibacter michiganensis subspecies michiganensis.
C. Revisions to Requested Exemption
In its petition, the petitioner requested generally that the Agency
issue an exemption from the requirement of a tolerance for residues of
bacteriophage of Clavibacter michiganensis subspecies michiganensis in
or on tomato. The petitioner's supporting materials indicated that the
actual pesticide that would be used would be safe because the
bacteriophage were lytic and produced in Clavibacter michiganensis
subspecies michiganensis. The Agency believes both that these two
conditions are necessary to make the safety finding and the petitioner
was only requesting a narrow exemption; therefore, the Agency is
modifying the tolerance exemption regulatory text to include such
criteria.
VIII. Conclusions
EPA concludes that there is a reasonable certainty that no harm
will result to the U.S. population, including infants and children,
from aggregate exposure to residues of lytic bacteriophage of
Clavibacter michiganensis subspecies michiganensis produced in
Clavibacter michiganensis subspecies michiganensis. Therefore, an
exemption from the requirement of a tolerance is established for
residues of lytic bacteriophage of Clavibacter michiganensis subspecies
michiganensis produced in Clavibacter michiganensis subspecies
michiganensis in or on tomato when applied as a bactericide in
accordance with good agricultural practices.
IX. References
1. Keel C, Ucurum Z, Michaux P, Adrian M, Haas D. 2002. Deleterious
impact of a virulent bacteriophage on survival and biocontrol
activity of Pseudomonas fluorescens strain CHAO in natural soil.
Molecular Plant-Microbe Interactions 15:567-576.
2. Liew KW, Alvarez AM. 1981. Biological and morphological
characterization of Xanthomonas campestris bacteriophages.
Phytopatholoy 71:269-273.
3. Demuth J, Neve H, Witzel K-P. 1993. Direct electron microscopy
study on the morphological diversity of bacteriophage populations in
Lake Plussse. Applied and Environmental Microbiology 59:3378-3384.
4. Eayre CG, Bartz JA, Concelmo DE. 1995. Bacteriophages of Erwinia
carotovora and Erwinia ananas isolated from freshwater lakes. Plant
Disease 79:801-804.
5. Schnabel EL, Jones AL. 2001. Isolation and characterization of
five Erwinia amylovora bacteriophages and assessment of phage
resistance in strains of Erwinia amylovora. Applied and
Environmental Microbiology 67:59-64.
6. Denis FA. 1975. Contamination of shellfish with strains of
Pseudomonas aeruginosa and specific bacteriophages. Canadian Journal
of Microbiology 21:1055-1057.
7. Merril CR, Scholl D, Adhya SL. 2003. The prospect for
bacteriophage therapy in Western medicine. Nature 2:489-497.
8. Rohwer F. 2003. Global phage diversity. Cell 113:1-2.
9. Stocker BAD. 1955. Bacteriophage and bacterial classification.
Journal of General Microbiology 12:375-381.
10. Duckworth DH, Gulig PA. 2002. Bacteriophage: potential treatment
for bacterial infections. Biodrugs 16:57-62.
11. Summers WC. 2001. Bacteriophage therapy. Annual Review of
Microbiology 55:437-451.
12. Lorch A. 1999. Bacteriophage: an alternative to antibiotics?
Biotechnology and Development Monitor 39:14-17.
13. Petricciani JC, Hsu TC, Stock AD, Turner JH, Wenger SL, Elisberg
BL. 1978. Bacteriophages, vaccines, and people: an assessment of
risk. Proceedings of the Society for Experimental Biology and
Medicine. 58:378-382.
14. Ackermann H-W. 1997. Bacteriophage ecology. Pp. 335-339 in:
``Progress in Microbial Ecology (Proceedings of Seventh
International Symposium on Microbial Ecology)''. Martins MT, Sato
MIZ, Tiedje JM, Hagler LCN, D[ouml]bereiner J, Sanchez PS, eds.
Brazilian Society for Microbiology.
15. Kennedy JE Jr, Wei CI, Oblinger JL. 1986. Methodology for
enumeration of coliphages in foods. Applied and Environmental
Microbiology 51:956-962.
16. Kennedy JE Jr, Oblinger JL, Bitton G. 1984. Recovery of
coliphages from chicken, pork sausage and delicatessen meats.
Journal of Food Protection 47:623-626.
17. DePaola A, Motes ML, Chan AM, Suttle CA. 1998. Phages infecting
Vibrio vulnificus are abundant and diverse in oysters (Crassostrea
virginica) collected from the Gulf of Mexico. Applied and
Environmental Microbiology 64:346-351.
18. Quiberoni A, Tremblay D, Ackermann H-W, Moineau S, Reinheimer
JA. 2006. Diversity of Streptococcus thermophilus phages in a large-
production cheese factory in Argentina. Journal of Dairy Science
89:3791-3799.
19. Guillaumes J, Houdeau G, Germain R, Olivier JM. 1988.
Improvement of the biocontrol of Pseudomonas tolaasii using
bacteriophages associated with an antagonistic bacterium. Bulletin
OEPP 18:77-82.
20. Radetsky P. 1996. The good virus. Discover 17:50-58.
21. Chanishvili N, Chanishvili T, Tediashvili M, Barrow PA. 2001.
Phages and their
[[Page 66192]]
application against drug-resistant bacteria. Journal of Chemical
Technology and Biotechnology 76:689-699.
22. U.S. EPA. 2011. Bacteriophage of Clavibacter michiganensis
subsp. michiganensis--AgriPhage CMM. Memorandum from J.V. Gagliardi,
Ph.D. to A. Gross dated June 30, 2011.
23. U.S. EPA. 2011. Bacteriophage of Clavibacter michiganensis
subspecies michiganensis Biopesticides Registration Action Document
dated August 25, 2011 (available as ``Supporting & Related
Material'' with docket ID number EPA-HQ-OPP2009-0539 at https://www.regulations.gov).
24. Atterbury RJ, Connerton PL, Dodd CER, Rees CED, Connerton IF.
2003. Isolation and characterization of Campylobacter bacteriophages
from retail poultry. Applied and Environmental Microbiology 69:4511-
4518.
25. Gautier M, Rouault A, Sommer P, Briandet R. 1995. Occurrence of
Propionibacterium freudenreichii bacteriophages in swiss cheese.
Applied and Environmental Microbiology 61:2572-2576.
26. Greer GG. 2005. Bacteriophage control of foodborne bacteria.
Journal of Food Protection 68:1102-1111.
27. Whitman PA, Marshall RT. 1971. Isolation of psychrophilic
bacteriophagehost systems from refrigerated food products. Applied
Microbiology 22:220-223.
28. El-Abagy MM, Dutka BJ, Kamel M. 1988. Incidence of coliphage in
potable water supplies. Applied and Environmental Microbiology
54:1632-1633.
X. Statutory and Executive Order Reviews
This final rule establishes a tolerance exemption under section
408(d) of FFDCA in response to a petition submitted to EPA. The Office
of Management and Budget (OMB) has exempted these types of actions from
review under Executive Order 12866, entitled Regulatory Planning and
Review (58 FR 51735, October 4, 1993). Because this final rule has been
exempted from review under Executive Order 12866, this final rule is
not subject to Executive Order 13211, entitled Actions Concerning
Regulations That Significantly Affect Energy Supply, Distribution, or
Use (66 FR 28355, May 22, 2001), or Executive Order 13045, entitled
Protection of Children from Environmental Health Risks and Safety Risks
(62 FR 19885, April 23, 1997). This final rule does not contain any
information collections subject to OMB approval under the Paperwork
Reduction Act (PRA), 44 U.S.C. 3501 et seq., nor does it require any
special considerations under Executive Order 12898, entitled Federal
Actions to Address Environmental Justice in Minority Populations and
Low-Income Populations (59 FR 7629, February 16, 1994).
Since tolerances and exemptions that are established on the basis
of a petition under section 408(d) of FFDCA, such as the tolerance
exemption in this final rule, do not require the issuance of a proposed
rule, the requirements of the Regulatory Flexibility Act (RFA) (5
U.S.C. 601 et seq.) do not apply.
This final rule directly regulates growers, food processors, food
handlers, and food retailers, not States or tribes. As a result, this
action does not alter the relationships or distribution of power and
responsibilities established by Congress in the preemption provisions
of section 408(n)(4) of FFDCA. As such, EPA has determined that this
action will not have a substantial direct effect on States or tribal
governments, on the relationship between the national government and
the States or tribal governments, or on the distribution of power and
responsibilities among the various levels of government or between the
Federal Government and Indian tribes. Thus, EPA has determined that
Executive Order 13132, entitled Federalism (64 FR 43255, August 10,
1999), and Executive Order 13175, entitled Consultation and
Coordination with Indian Tribal Governments (65 FR 67249, November 9,
2000), do not apply to this final rule. In addition, this final rule
does not impose any enforceable duty or contain any unfunded mandate as
described under Title II of the Unfunded Mandates Reform Act of 1995
(UMRA) (Pub. L. 104-4).
This action does not involve any technical standards that would
require EPA consideration of voluntary consensus standards pursuant to
section 12(d) of the National Technology Transfer and Advancement Act
of 1995 (NTTAA), Public Law 104-113, section 12(d) (15 U.S.C. 272
note).
XI. Congressional Review Act
The Congressional Review Act, 5 U.S.C. 801 et seq., generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report to each House of the Congress and to
the Comptroller General of the United States. EPA will submit a report
containing this rule and other required information to the U.S. Senate,
the U.S. House of Representatives, and the Comptroller General of the
United States prior to publication of this final rule in the Federal
Register. This final rule is not a ``major rule'' as defined by 5
U.S.C. 804(2).
List of Subjects in 40 CFR Part 180
Environmental protection, Administrative practice and procedure,
Agricultural commodities, Pesticides and pests, Reporting and
recordkeeping requirements.
Dated: September 30, 2011.
Steven Bradbury,
Director, Office of Pesticide Programs.
Therefore, 40 CFR chapter I is amended as follows:
PART 180--[AMENDED]
0
1. The authority citation for part 180 continues to read as follows:
Authority: 21 U.S.C. 321(q), 346a and 371.
0
2. Section 180.1307 is added to subpart D to read as follows:
Sec. 180.1307 Bacteriophage of Clavibacter michiganensis subspecies
michiganensis; exemption from the requirement of a tolerance.
An exemption from the requirement of a tolerance is established for
residues of lytic bacteriophage of Clavibacter michiganensis subspecies
michiganensis produced in Clavibacter michiganensis subspecies
michiganensis in or on tomato when applied as a bactericide in
accordance with good agricultural practices.
[FR Doc. 2011-27042 Filed 10-25-11; 8:45 am]
BILLING CODE 6560-50-P