Endangered and Threatened Wildlife and Plants; 90-Day Finding on a Petition To Delist the Wood Bison, 23533-23536 [2013-09241]
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Federal Register / Vol. 78, No. 76 / Friday, April 19, 2013 / Proposed Rules
a standardized Network Access Code
(NAC) by rule for operation on the 700
MHz interoperability channels. The
NAC is a pre-programmed digital
address in a Project 25 radio which
allows the radio to ‘‘hear’’ only
communications directed to that
address from another radio. If the NAC
is to be set by rule, the NPRM seeks
comment what code would be most
appropriate. Alternatively, the NPRM
seeks comment on whether NACs
should be left to an industry standard,
which would be more flexible then
codifying a single code into the
Commission’s rules.
31. User Access to Interoperability
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MHz band be capable of being
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of the 6.25 kilohertz bandwidth
interoperability channels. The NPRM
seeks comment on its proposal.
32. Analog Operation on the
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portable equipment in analog mode on
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benefits may accrue from allowing
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G. Federal Rules That May Duplicate,
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Ordering Clauses
34. Accordingly, it is ordered that,
pursuant to sections 1, 4(i), 303, 316,
332 and 337 of the Communications Act
of 1934, as amended, 47 U.S.C. 151,
154(i), 303, 316, 332 and 337, the NPRM
is hereby adopted.
35. It is further ordered that pursuant
to applicable procedures set forth in
§§ 1.415 and 1.419 of the Commission’s
rules, 47 CFR 1.415, 1.419, interested
parties may file comments on the NPRM
on or before June 18, 2013, and reply
comments on or before July 18, 2013.
36. It is further ordered that the
Commission shall send a copy of the
NPRM in a report to be sent to Congress
and the General Accounting Office
pursuant to the Congressional Review
Act, 5 U.S.C. 801(a)(1)(A).
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Federal Communications Commission.
Marlene H. Dortch,
Secretary.
Information Relay Service (FIRS) at
800–877–8339.
SUPPLEMENTARY INFORMATION:
[FR Doc. 2013–09069 Filed 4–18–13; 8:45 am]
Background
Section 4(b)(3)(A) of the Act (16
U.S.C. 1531 et seq.) requires that we
make a finding on whether a petition to
list, delist, or reclassify a species
presents substantial scientific or
commercial information indicating that
the petitioned action may be warranted.
We are to base this finding on
information provided in the petition,
supporting information submitted with
the petition, and information otherwise
available in our files. To the maximum
extent practicable, we are to make this
finding within 90 days of our receipt of
the petition, and publish our notice of
the finding promptly in the Federal
Register.
Our standard for substantial scientific
or commercial information within the
Code of Federal Regulations (CFR) with
regard to a 90-day petition finding is
‘‘that amount of information that would
lead a reasonable person to believe that
the measure proposed in the petition
may be warranted’’ (50 CFR 424.14(b)).
If we find that substantial scientific or
commercial information was presented,
we are required to promptly conduct a
species status review, which we
subsequently summarize in our 12month finding.
BILLING CODE 6712–01–P
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[Docket No. FWS–HQ–ES–2012–0094;
FXES111309F2130–123–FF09E22000]
Endangered and Threatened Wildlife
and Plants; 90-Day Finding on a
Petition To Delist the Wood Bison
Fish and Wildlife Service,
Interior.
ACTION: Notice of 90-day petition
finding.
AGENCY:
We, the U.S. Fish and
Wildlife Service (Service), announce a
90-day finding on a petition to delist the
wood bison (Bison bison athabascae)
under the Endangered Species Act of
1973, as amended (Act). Based on our
review, we find that the petition does
not present substantial information
indicating that delisting the wood bison
subspecies may be warranted.
Therefore, we are not initiating a status
review in response to this petition.
However, we ask the public to submit to
us any new information that becomes
available concerning the status of, or
threats to, the wood bison or its habitat
at any time.
DATES: The finding announced in this
document was made on April 19, 2013.
ADDRESSES: This finding is available on
the Internet at https://
www.regulations.gov at Docket Number
FWS–HQ–ES–2012–0094. Supporting
documentation we used in preparing
this finding is available for public
inspection, by appointment, during
normal business hours at the U.S. Fish
and Wildlife Service, Alaska Regional
Office, 1011 East Tudor Road,
Anchorage, AK 99503; (907) 786–3856.
Please submit any new information,
materials, comments, or questions
concerning this finding to the above
street address.
FOR FURTHER INFORMATION CONTACT:
Marilyn Myers at U.S. Fish and Wildlife
Service, Fisheries and Ecological
Services, 1011 E. Tudor Road,
Anchorage, AK 99503; or by telephone
at 907–786–3559; or by facsimile at
(907) 786–3848. If you use a
telecommunications device for the deaf
(TDD), please call the Federal
SUMMARY:
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Petition History
On April 3, 2012, we received a
petition, dated April 3, 2012, from the
Western Bison Association, the Rocky
Mountain Buffalo Association, the
Minnesota Buffalo Association, the
Oklahoma Buffalo Association, the
North Dakota Buffalo Association, the
Northwest Buffalo Association, the
Missouri Buffalo Association, the
Kansas Buffalo Association, and W.
Michael Gear and Kathleen O’Neal Gear
requesting that the wood bison be
removed from the Federal List of
Endangered and Threatened Wildlife as
threatened under the Act. The petition
clearly identified itself as such and
included the requisite identification
information for the petitioners, as
required at 50 CFR 424.14(a). In a letter
to the petitioners sent April 24, 2012,
we stated that we anticipated that we
would review the petition and make a
finding within the coming year. This
finding addresses the petition.
Previous Federal Action(s)
The listing history for wood bison is
extensive and was reconstructed in the
proposed rule to reclassify wood bison
from endangered to threatened, which
published February 8, 2011 (76 FR
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6734). Please refer to that document for
the complete listing history. Here we
present only the most pertinent facts.
Wood bison became listed in the
United States under the 1969
Endangered Species Conservation Act
when it was included on the first List
of Endangered Foreign Fish and
Wildlife, which was published in the
Federal Register on June 2, 1970 (35 FR
8491). In 1974, the first list under the
1973 Endangered Species Act appeared
in the Code of Federal Regulations
(CFR); the wood bison was listed as an
endangered species based on its
inclusion on the original 1969 list.
Because the wood bison was listed
under the 1969 Endangered Species
Conservation Act, there is not a separate
Federal Register notice that defined the
population(s) and their range, or
analyzed threats to the subspecies.
On May 14, 1998, the Service received
a petition from a private individual
requesting that the Service remove the
wood bison from the List of Endangered
and Threatened Wildlife, primarily
because it had been downlisted from
Appendix I to Appendix II under the
Convention on International Trade in
Endangered Species of Wild Fauna and
Flora (CITES). In a 90-day finding
published on November 25, 1998 (63 FR
65164), we found that the petitioner did
not provide substantial information to
indicate that the delisting may be
warranted.
On November 26, 2007, we received
a petition from the co-chairs of Canada’s
National Wood Bison Recovery Team
requesting that we reclassify the wood
bison from endangered to threatened.
On February 3, 2009, we published a 90day finding (74 FR 5908) acknowledging
that the petition provided sufficient
information to indicate that
reclassification may be warranted and
that we would initiate a status review.
On February 8, 2011, we published a
proposed rule to reclassify wood bison
(76 FR 6734), and on May 3, 2012, we
published a final rule reclassifying
wood bison as threatened under the Act
(77 FR 26191).
Status in Canada
In Canada, the Species at Risk Act
(SARA) is the Canadian counterpart to
the U.S. Endangered Species Act. Under
the SARA, the Committee on the Status
of Endangered Wildlife in Canada
(COSEWIC) was established as the
scientific body that identifies and
assesses a species’ status. The wood
bison was recognized by the COSEWIC
as an endangered subspecies of
Canadian wildlife in 1978. Wood bison
was reclassified to threatened in June
1988, based on a status report prepared
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by the National Wood Bison Recovery
Team. The National Wood Bison
Recovery Team published a national
recovery plan in 2001 (Gates et al.
2001), which has guided recovery
actions in Canada since that time.
Species Information
Wood bison is the largest native
extant terrestrial mammal in North
America (Reynolds et al. 2003, p. 1015).
Average weight of mature males (age 8)
is 910 kilograms (kg) (2,006 pounds (lb))
and the average weight of mature
females (age 13) is 440 kg (970 lb)
(Reynolds et al. 2003, p. 1015). They
have a large triangular head, a thin
beard and rudimentary throat mane, and
a poorly demarcated cape (Boyd et al.
2010, p. 16). In addition, the highest
point of their hump is forward of their
front legs; they have reduced chaps on
their front legs; and their horns usually
extend above the hair on their head
(Boyd et al. 2010, p. 16). These physical
characteristics distinguish them from
the plains bison (Reynolds et al. 2003,
p. 1015; Boyd et al. 2010, p. 16).
Detailed information on the biology of
wood bison is provided in our February
8, 2011, proposed rule to reclassify
wood bison as threatened (76 FR 6734)
and in our May 3, 2012, final rule (77
FR 26191). Please refer to those
documents for a detailed account of the
species’ biology.
Taxonomy
In the proposed and final rules (76 FR
6734, 77 FR 26191), we adopt the
widely accepted notion that wood bison
is a valid subspecies, a point which the
petitioners contest. The petitioners
assert that wood bison and plains bison
(Bison bison bison) are not significantly
different and that they should be
considered a single species. Therefore,
we discuss taxonomic classification and
our rationale for accepting wood bison
as a valid subspecies below.
Taxonomy is the theory and practice
of classifying organisms. Traditionally,
physical characteristics of an organism
were used to describe a species.
However, from an evolutionary
perspective, appearances can be
deceptive; animals that look alike may
not be closely related and animals that
appear different from one another may
actually be closely related. With the
advent of sophisticated molecular tools,
taxonomists can now examine various
aspects of a species genetic code to help
them determine how closely animals are
related to one another. Although
molecular techniques have added
another tool in the taxonomist’s toolbox,
they also have limitations and do not
necessarily give an unambiguous
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picture of the relationship among
species. Sample size (number of animals
sampled, number of genes sampled, or
the number of loci on a gene sampled),
type of DNA examined (mitochondrial
DNA vs. nuclear DNA), the techniques
used, and the populations selected for
sampling are among a few of the reasons
that variable or ambiguous results may
arise. In addition, how a species (or
subspecies) is defined, which on its face
is a simple concept, is in reality very
complex, and several definitions for
‘‘species’’ exist (Mayr and Ashlock
1991, pp. 24–28; de Queiroz 2007, pp.
879–885). Consequently, the
intersection of incomplete knowledge of
exactly how animals are related to one
another, combined with the human
concept of what a species is, often
culminates in controversy over whether
certain groups of animals should be
lumped together or split apart. Such is
the case for wood bison.
We recognize, as the petitioners
assert, that differences in opinion exist
regarding the division of Bison into two
subspecies (B. b. athabascae and B. b.
bison) (e.g., Bork et al. 1991, pp. 43, 47;
Geist 1991, p. 283). However, quantified
differences in pelage (e.g., distribution
of mane, chaps, and cape) and structure
(e.g., overall body size, location of
hump, length of horns) have been
described (van Zyll de Jong et al. 1995,
pp. 394–400). These differences, and the
fact that wood bison and plains bison
are physically separated by a great
distance, led Boyd et al. (2010, p. 16
(American Bison Specialist Group)) to
conclude separation into two subspecies
is consistent with the subspecies
concept. As noted in our final rule to
downlist wood bison (77 FR 26209), the
introduction of plains bison into Wood
Buffalo National Park in Canada, the
only place where wood bison remained
in the 1920s, led to some degree of
hybridization. However, genetic
analysis has indicated that although the
wood bison had limited contact with
plains bison, it was minimal enough
that the animals exhibit predominantly
wood bison traits. Wood bison
originating from founders with minimal
contact with plains bison are genetically
more similar to one another than they
are to plains bison (van Zyll de Jong et
al. 1995, pp. 394–404; Wilson and
Strobeck 1999, p. 493). Hybridization
did not lead to a phenotypically
homogenous population (one
population that looks the same) (van
Zyll de Jong et al. 1995, pp. 394–404).
As described above, molecular tools
can be used to evaluate the relatedness
of individuals, populations, species, and
genera. The work of Wilson (2001) and
Wilson and Strobeck (1999, pp. 493–
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494) using DNA microsatellites indicate
that the genetic differences between
plains bison and wood bison are greater
than those within either of the two
subspecies. These results support
maintaining the subspecific designation.
Results of studies that sequence only
mitochondrial DNA are of limited value
in answering questions about
subspecific designation because
mitochondrial DNA is inherited only
from the maternal side (Avise 1994, pp.
62, 99). In the case of Douglas et al.
(2011), which the petitioners use as
support for their argument of lumping
the subspecies together, mitochondrial
DNA from only two wood bison were
sequenced, further limiting the authors’
ability to draw general conclusions
about the relatedness of wood and
plains bison. As Boyd et al. (2010, p. 17)
note, the inability to detect a difference
with a molecular test comparing limited
sequences of genomic material does not
necessarily mean that there is no
difference. It is possible that in the
future refined genetic analysis with
appropriate sample design and sample
size will provide a more compelling
reason to lump the two subspecies
together. Until that time, we will
continue to follow the accepted
separation of North American bison into
two subspecies.
The Canadian National Recovery Plan
(Gates et al. 2001, p. 28) provides this
summary about American bison
subspecies:
(1) Historically, wood bison differed
from other bison populations with
regard to multiple morphological and
genetic characteristics.
(2) The intrusion of plains bison into
the range of wood bison in 1925–1928
was entirely human-caused.
(3) The two North American bison
subspecies continue to be
morphologically and genetically
distinct, despite some hybridization in
the 1920s.
(4) Wood bison and their descendants
continue to constitute populations of a
subspecies of bison.
In a recent evaluation of the
subspecific separation of wood bison
from plains bison, Boyd et al. (2010 pp.
15–18) also conclude that there appears
to be sufficient justification for the
formal recognition of the two
subspecies. In addition, they point out
that regardless of the formal designation
for wood bison, all forms of geographic
and ecological variation contribute to
biodiversity and that variants of a
species may have evolutionarily
important ecological adaptations (Boyd
et al. 2010, p. 18). This reality is
reflected in the Service’s ability to
recognize and provide protection to
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‘‘distinct population segments’’ at a
taxonomic level below subspecies. In
addition, COSEWIC also considers and
includes subspecies, varieties, or
geographically or genetically distinct
populations in its definition of wildlife
species (https://www.cosewic.gc.ca/eng/
sct2/sct2_5_e.cfm, viewed June 26,
2012). Both the Act and SARA recognize
that conservation of biological diversity
requires protection for taxonomic
entities below the species level whether
at the subspecific level or less (e.g.,
distinct populations). Therefore,
regardless of how we name the
populations we now call wood bison,
since its description in 1897 (Rhoads
1897) wood bison in Canada have been
recognized as a unique subspecies and
managed as such. Consequently, even if
we were to consider wood bison and
plains bison as one species, that would
not automatically lead to the delisting of
the wood bison.
The International Code of Zoological
Nomenclature (Code) provides guidance
to zoologists worldwide regarding
naming species. In the Preface to the
Code it states, ‘‘Nomenclatural rules are
tools that are designed to provide the
maximum stability compatible with
taxonomic freedom.’’ A published
‘‘revision’’ or ‘‘monograph’’ is the
standard method used to examine all
the species within a group and present
a unified synopsis of all of the
information available (Mayr and
Ashlock 1991, p. 348). Recognizing the
taxonomic controversy that exists for
the subspecific designation of wood
bison, a reasonable, defensible, and
conservative approach is to follow the
naming conventions that are in place.
The petition does not provide
compelling, convincing, or
unambiguous information that would
cause the Service to consider wood
bison and plains bison as a single
species, nor can we authoritatively
resolve this issue with the information
available.
In summary, based on the historical
physical separation, and quantifiable
behavioral, morphological, phenological
(appearance), and genetic differences
between the two subspecies, the best
available scientific information
indicates that subspecific designation is
appropriate (FEAP 1990, p. 24; Bork et
al. 1991, p. 47; van Zyll de Jong et al.
1995, pp. 403–404; Wilson and Strobeck
1999, pp. 492–494; Reynolds et al. 2003,
p. 1010; Boyd et al. 2010, pp. 15–18).
The established management of bison as
two subspecies and the long-standing
recognition of the two subspecies by the
scientific community provide additional
justification for treating wood bison and
plains bison as two distinct subspecies.
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23535
Evaluation of Information for This
Finding
Section 4 of the Act (16 U.S.C. 1533)
and its implementing regulations at 50
CFR part 424 set forth the procedures
for adding a species to, or removing a
species from, the Federal Lists of
Endangered and Threatened Wildlife
and Plants. A species may be
determined to be an endangered or
threatened species due to one or more
of the five factors described in section
4(a)(1) of the Act:
(A) The present or threatened
destruction, modification, or
curtailment of its habitat or range;
(B) Overutilization for commercial,
recreational, scientific, or educational
purposes;
(C) Disease or predation;
(D) The inadequacy of existing
regulatory mechanisms; or
(E) Other natural or manmade factors
affecting its continued existence.
We must consider these same five
factors in delisting a species. We may
delist a species according to 50 CFR
424.11(d) if the best available scientific
and commercial data indicate that the
species is neither endangered nor
threatened for the following reasons:
(1) The species is extinct;
(2) The species has recovered and is
no longer endangered or threatened; or
(3) The original scientific data used at
the time the species was classified were
in error.
In the case of this petition, the
petitioners have not discussed threats to
the species (or subspecies) that remain
or have been eliminated. They focus
instead on the success of recovery
efforts for wood bison ‘‘ecotype,’’ the
increase in the number of animals, and
the establishment of new herds. We
agree that significant strides have been
made towards recovery of wood bison,
and we discussed the success of
recovery efforts in our proposed and
final rules for the reclassification of
wood bison (76 FR 6734, 77 FR 26191).
Although we acknowledge that wood
bison are no longer endangered, we
conclude in our final rule that threats to
wood bison remain and that the wood
bison should be listed as threatened. In
particular, we identified loss of habitat,
disease, and hybridization as ongoing
threats. The conclusions made in the
May 3, 2012, final rule to reclassify the
subspecies are still valid. The
petitioners have not provided, and we
have not received, any new information
regarding threats to, or recovery of,
wood bison that was not considered in
the final reclassification rule.
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Finding
which published earlier this year, we
identified threats that remain to the
species. The petitioners did not provide
any new information about the status of
the species that we were not already
aware of and had evaluated in our final
rule.
On the basis of our determination
under section 4(b)(3)(A) of the Act, we
conclude that the petition does not
present substantial scientific or
commercial information to indicate that
delisting the wood bison under the Act
may be warranted at this time. Although
we will not conduct a thorough review
of the status of the species at this time,
we encourage interested parties to
continue to gather data that will assist
with the conservation of the wood
bison. If you wish to provide
information regarding the wood bison,
you may submit your information or
materials to Marilyn Myers, Endangered
Species Biologist, Alaska Regional
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The petition does not present
substantial information to indicate that
delisting of wood bison is warranted.
Although we recognize that controversy
exists around the subspecific
designation for wood bison,
nomenclature stability, management
history, and the acceptance of two
subspecies by the American Bison
Specialist Group, the Canadian National
Wood Bison Recovery Team, and other
zoologists lead us to the conclusion that
retaining the current nomenclature is
appropriate and defensible.
Although the petitioners argue that
wood bison and plains bison should be
considered as one species, they did not
indicate that all or most threats to bison
have been ameliorated. Instead, they
focus on the success of recovery efforts
for wood bison. We agree that the status
of wood bison is more secure today than
it once was. However, in our final rule
to reclassify wood bison as threatened,
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Office (see FOR FURTHER INFORMATION
at any time.
CONTACT),
References Cited
A complete list of references cited is
available on the Internet at https://
www.regulations.gov and upon request
from the Alaska Regional Office (see FOR
FURTHER INFORMATION CONTACT).
Author
The primary author of this notice is
Marilyn Myers of the Alaska Regional
Office (see FOR FURTHER INFORMATION
CONTACT).
Authority
The authority for this action is the
Endangered Species Act of 1973, as
amended (16 U.S.C. 1531 et seq.).
Dated: November 7, 2012.
Daniel M. Ashe,
Director, U.S. Fish and Wildlife Service.
[FR Doc. 2013–09241 Filed 4–18–13; 8:45 am]
BILLING CODE 4310–55–P
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Agencies
[Federal Register Volume 78, Number 76 (Friday, April 19, 2013)]
[Proposed Rules]
[Pages 23533-23536]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2013-09241]
=======================================================================
-----------------------------------------------------------------------
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[Docket No. FWS-HQ-ES-2012-0094; FXES111309F2130-123-FF09E22000]
Endangered and Threatened Wildlife and Plants; 90-Day Finding on
a Petition To Delist the Wood Bison
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Notice of 90-day petition finding.
-----------------------------------------------------------------------
SUMMARY: We, the U.S. Fish and Wildlife Service (Service), announce a
90-day finding on a petition to delist the wood bison (Bison bison
athabascae) under the Endangered Species Act of 1973, as amended (Act).
Based on our review, we find that the petition does not present
substantial information indicating that delisting the wood bison
subspecies may be warranted. Therefore, we are not initiating a status
review in response to this petition. However, we ask the public to
submit to us any new information that becomes available concerning the
status of, or threats to, the wood bison or its habitat at any time.
DATES: The finding announced in this document was made on April 19,
2013.
ADDRESSES: This finding is available on the Internet at https://www.regulations.gov at Docket Number FWS-HQ-ES-2012-0094. Supporting
documentation we used in preparing this finding is available for public
inspection, by appointment, during normal business hours at the U.S.
Fish and Wildlife Service, Alaska Regional Office, 1011 East Tudor
Road, Anchorage, AK 99503; (907) 786-3856. Please submit any new
information, materials, comments, or questions concerning this finding
to the above street address.
FOR FURTHER INFORMATION CONTACT: Marilyn Myers at U.S. Fish and
Wildlife Service, Fisheries and Ecological Services, 1011 E. Tudor
Road, Anchorage, AK 99503; or by telephone at 907-786-3559; or by
facsimile at (907) 786-3848. If you use a telecommunications device for
the deaf (TDD), please call the Federal Information Relay Service
(FIRS) at 800-877-8339.
SUPPLEMENTARY INFORMATION:
Background
Section 4(b)(3)(A) of the Act (16 U.S.C. 1531 et seq.) requires
that we make a finding on whether a petition to list, delist, or
reclassify a species presents substantial scientific or commercial
information indicating that the petitioned action may be warranted. We
are to base this finding on information provided in the petition,
supporting information submitted with the petition, and information
otherwise available in our files. To the maximum extent practicable, we
are to make this finding within 90 days of our receipt of the petition,
and publish our notice of the finding promptly in the Federal Register.
Our standard for substantial scientific or commercial information
within the Code of Federal Regulations (CFR) with regard to a 90-day
petition finding is ``that amount of information that would lead a
reasonable person to believe that the measure proposed in the petition
may be warranted'' (50 CFR 424.14(b)). If we find that substantial
scientific or commercial information was presented, we are required to
promptly conduct a species status review, which we subsequently
summarize in our 12-month finding.
Petition History
On April 3, 2012, we received a petition, dated April 3, 2012, from
the Western Bison Association, the Rocky Mountain Buffalo Association,
the Minnesota Buffalo Association, the Oklahoma Buffalo Association,
the North Dakota Buffalo Association, the Northwest Buffalo
Association, the Missouri Buffalo Association, the Kansas Buffalo
Association, and W. Michael Gear and Kathleen O'Neal Gear requesting
that the wood bison be removed from the Federal List of Endangered and
Threatened Wildlife as threatened under the Act. The petition clearly
identified itself as such and included the requisite identification
information for the petitioners, as required at 50 CFR 424.14(a). In a
letter to the petitioners sent April 24, 2012, we stated that we
anticipated that we would review the petition and make a finding within
the coming year. This finding addresses the petition.
Previous Federal Action(s)
The listing history for wood bison is extensive and was
reconstructed in the proposed rule to reclassify wood bison from
endangered to threatened, which published February 8, 2011 (76 FR
[[Page 23534]]
6734). Please refer to that document for the complete listing history.
Here we present only the most pertinent facts.
Wood bison became listed in the United States under the 1969
Endangered Species Conservation Act when it was included on the first
List of Endangered Foreign Fish and Wildlife, which was published in
the Federal Register on June 2, 1970 (35 FR 8491). In 1974, the first
list under the 1973 Endangered Species Act appeared in the Code of
Federal Regulations (CFR); the wood bison was listed as an endangered
species based on its inclusion on the original 1969 list. Because the
wood bison was listed under the 1969 Endangered Species Conservation
Act, there is not a separate Federal Register notice that defined the
population(s) and their range, or analyzed threats to the subspecies.
On May 14, 1998, the Service received a petition from a private
individual requesting that the Service remove the wood bison from the
List of Endangered and Threatened Wildlife, primarily because it had
been downlisted from Appendix I to Appendix II under the Convention on
International Trade in Endangered Species of Wild Fauna and Flora
(CITES). In a 90-day finding published on November 25, 1998 (63 FR
65164), we found that the petitioner did not provide substantial
information to indicate that the delisting may be warranted.
On November 26, 2007, we received a petition from the co-chairs of
Canada's National Wood Bison Recovery Team requesting that we
reclassify the wood bison from endangered to threatened. On February 3,
2009, we published a 90-day finding (74 FR 5908) acknowledging that the
petition provided sufficient information to indicate that
reclassification may be warranted and that we would initiate a status
review. On February 8, 2011, we published a proposed rule to reclassify
wood bison (76 FR 6734), and on May 3, 2012, we published a final rule
reclassifying wood bison as threatened under the Act (77 FR 26191).
Status in Canada
In Canada, the Species at Risk Act (SARA) is the Canadian
counterpart to the U.S. Endangered Species Act. Under the SARA, the
Committee on the Status of Endangered Wildlife in Canada (COSEWIC) was
established as the scientific body that identifies and assesses a
species' status. The wood bison was recognized by the COSEWIC as an
endangered subspecies of Canadian wildlife in 1978. Wood bison was
reclassified to threatened in June 1988, based on a status report
prepared by the National Wood Bison Recovery Team. The National Wood
Bison Recovery Team published a national recovery plan in 2001 (Gates
et al. 2001), which has guided recovery actions in Canada since that
time.
Species Information
Wood bison is the largest native extant terrestrial mammal in North
America (Reynolds et al. 2003, p. 1015). Average weight of mature males
(age 8) is 910 kilograms (kg) (2,006 pounds (lb)) and the average
weight of mature females (age 13) is 440 kg (970 lb) (Reynolds et al.
2003, p. 1015). They have a large triangular head, a thin beard and
rudimentary throat mane, and a poorly demarcated cape (Boyd et al.
2010, p. 16). In addition, the highest point of their hump is forward
of their front legs; they have reduced chaps on their front legs; and
their horns usually extend above the hair on their head (Boyd et al.
2010, p. 16). These physical characteristics distinguish them from the
plains bison (Reynolds et al. 2003, p. 1015; Boyd et al. 2010, p. 16).
Detailed information on the biology of wood bison is provided in our
February 8, 2011, proposed rule to reclassify wood bison as threatened
(76 FR 6734) and in our May 3, 2012, final rule (77 FR 26191). Please
refer to those documents for a detailed account of the species'
biology.
Taxonomy
In the proposed and final rules (76 FR 6734, 77 FR 26191), we adopt
the widely accepted notion that wood bison is a valid subspecies, a
point which the petitioners contest. The petitioners assert that wood
bison and plains bison (Bison bison bison) are not significantly
different and that they should be considered a single species.
Therefore, we discuss taxonomic classification and our rationale for
accepting wood bison as a valid subspecies below.
Taxonomy is the theory and practice of classifying organisms.
Traditionally, physical characteristics of an organism were used to
describe a species. However, from an evolutionary perspective,
appearances can be deceptive; animals that look alike may not be
closely related and animals that appear different from one another may
actually be closely related. With the advent of sophisticated molecular
tools, taxonomists can now examine various aspects of a species genetic
code to help them determine how closely animals are related to one
another. Although molecular techniques have added another tool in the
taxonomist's toolbox, they also have limitations and do not necessarily
give an unambiguous picture of the relationship among species. Sample
size (number of animals sampled, number of genes sampled, or the number
of loci on a gene sampled), type of DNA examined (mitochondrial DNA vs.
nuclear DNA), the techniques used, and the populations selected for
sampling are among a few of the reasons that variable or ambiguous
results may arise. In addition, how a species (or subspecies) is
defined, which on its face is a simple concept, is in reality very
complex, and several definitions for ``species'' exist (Mayr and
Ashlock 1991, pp. 24-28; de Queiroz 2007, pp. 879-885). Consequently,
the intersection of incomplete knowledge of exactly how animals are
related to one another, combined with the human concept of what a
species is, often culminates in controversy over whether certain groups
of animals should be lumped together or split apart. Such is the case
for wood bison.
We recognize, as the petitioners assert, that differences in
opinion exist regarding the division of Bison into two subspecies (B.
b. athabascae and B. b. bison) (e.g., Bork et al. 1991, pp. 43, 47;
Geist 1991, p. 283). However, quantified differences in pelage (e.g.,
distribution of mane, chaps, and cape) and structure (e.g., overall
body size, location of hump, length of horns) have been described (van
Zyll de Jong et al. 1995, pp. 394-400). These differences, and the fact
that wood bison and plains bison are physically separated by a great
distance, led Boyd et al. (2010, p. 16 (American Bison Specialist
Group)) to conclude separation into two subspecies is consistent with
the subspecies concept. As noted in our final rule to downlist wood
bison (77 FR 26209), the introduction of plains bison into Wood Buffalo
National Park in Canada, the only place where wood bison remained in
the 1920s, led to some degree of hybridization. However, genetic
analysis has indicated that although the wood bison had limited contact
with plains bison, it was minimal enough that the animals exhibit
predominantly wood bison traits. Wood bison originating from founders
with minimal contact with plains bison are genetically more similar to
one another than they are to plains bison (van Zyll de Jong et al.
1995, pp. 394-404; Wilson and Strobeck 1999, p. 493). Hybridization did
not lead to a phenotypically homogenous population (one population that
looks the same) (van Zyll de Jong et al. 1995, pp. 394-404).
As described above, molecular tools can be used to evaluate the
relatedness of individuals, populations, species, and genera. The work
of Wilson (2001) and Wilson and Strobeck (1999, pp. 493-
[[Page 23535]]
494) using DNA microsatellites indicate that the genetic differences
between plains bison and wood bison are greater than those within
either of the two subspecies. These results support maintaining the
subspecific designation. Results of studies that sequence only
mitochondrial DNA are of limited value in answering questions about
subspecific designation because mitochondrial DNA is inherited only
from the maternal side (Avise 1994, pp. 62, 99). In the case of Douglas
et al. (2011), which the petitioners use as support for their argument
of lumping the subspecies together, mitochondrial DNA from only two
wood bison were sequenced, further limiting the authors' ability to
draw general conclusions about the relatedness of wood and plains
bison. As Boyd et al. (2010, p. 17) note, the inability to detect a
difference with a molecular test comparing limited sequences of genomic
material does not necessarily mean that there is no difference. It is
possible that in the future refined genetic analysis with appropriate
sample design and sample size will provide a more compelling reason to
lump the two subspecies together. Until that time, we will continue to
follow the accepted separation of North American bison into two
subspecies.
The Canadian National Recovery Plan (Gates et al. 2001, p. 28)
provides this summary about American bison subspecies:
(1) Historically, wood bison differed from other bison populations
with regard to multiple morphological and genetic characteristics.
(2) The intrusion of plains bison into the range of wood bison in
1925-1928 was entirely human-caused.
(3) The two North American bison subspecies continue to be
morphologically and genetically distinct, despite some hybridization in
the 1920s.
(4) Wood bison and their descendants continue to constitute
populations of a subspecies of bison.
In a recent evaluation of the subspecific separation of wood bison
from plains bison, Boyd et al. (2010 pp. 15-18) also conclude that
there appears to be sufficient justification for the formal recognition
of the two subspecies. In addition, they point out that regardless of
the formal designation for wood bison, all forms of geographic and
ecological variation contribute to biodiversity and that variants of a
species may have evolutionarily important ecological adaptations (Boyd
et al. 2010, p. 18). This reality is reflected in the Service's ability
to recognize and provide protection to ``distinct population segments''
at a taxonomic level below subspecies. In addition, COSEWIC also
considers and includes subspecies, varieties, or geographically or
genetically distinct populations in its definition of wildlife species
(https://www.cosewic.gc.ca/eng/sct2/sct2_5_e.cfm, viewed June 26,
2012). Both the Act and SARA recognize that conservation of biological
diversity requires protection for taxonomic entities below the species
level whether at the subspecific level or less (e.g., distinct
populations). Therefore, regardless of how we name the populations we
now call wood bison, since its description in 1897 (Rhoads 1897) wood
bison in Canada have been recognized as a unique subspecies and managed
as such. Consequently, even if we were to consider wood bison and
plains bison as one species, that would not automatically lead to the
delisting of the wood bison.
The International Code of Zoological Nomenclature (Code) provides
guidance to zoologists worldwide regarding naming species. In the
Preface to the Code it states, ``Nomenclatural rules are tools that are
designed to provide the maximum stability compatible with taxonomic
freedom.'' A published ``revision'' or ``monograph'' is the standard
method used to examine all the species within a group and present a
unified synopsis of all of the information available (Mayr and Ashlock
1991, p. 348). Recognizing the taxonomic controversy that exists for
the subspecific designation of wood bison, a reasonable, defensible,
and conservative approach is to follow the naming conventions that are
in place. The petition does not provide compelling, convincing, or
unambiguous information that would cause the Service to consider wood
bison and plains bison as a single species, nor can we authoritatively
resolve this issue with the information available.
In summary, based on the historical physical separation, and
quantifiable behavioral, morphological, phenological (appearance), and
genetic differences between the two subspecies, the best available
scientific information indicates that subspecific designation is
appropriate (FEAP 1990, p. 24; Bork et al. 1991, p. 47; van Zyll de
Jong et al. 1995, pp. 403-404; Wilson and Strobeck 1999, pp. 492-494;
Reynolds et al. 2003, p. 1010; Boyd et al. 2010, pp. 15-18). The
established management of bison as two subspecies and the long-standing
recognition of the two subspecies by the scientific community provide
additional justification for treating wood bison and plains bison as
two distinct subspecies.
Evaluation of Information for This Finding
Section 4 of the Act (16 U.S.C. 1533) and its implementing
regulations at 50 CFR part 424 set forth the procedures for adding a
species to, or removing a species from, the Federal Lists of Endangered
and Threatened Wildlife and Plants. A species may be determined to be
an endangered or threatened species due to one or more of the five
factors described in section 4(a)(1) of the Act:
(A) The present or threatened destruction, modification, or
curtailment of its habitat or range;
(B) Overutilization for commercial, recreational, scientific, or
educational purposes;
(C) Disease or predation;
(D) The inadequacy of existing regulatory mechanisms; or
(E) Other natural or manmade factors affecting its continued
existence.
We must consider these same five factors in delisting a species. We
may delist a species according to 50 CFR 424.11(d) if the best
available scientific and commercial data indicate that the species is
neither endangered nor threatened for the following reasons:
(1) The species is extinct;
(2) The species has recovered and is no longer endangered or
threatened; or
(3) The original scientific data used at the time the species was
classified were in error.
In the case of this petition, the petitioners have not discussed
threats to the species (or subspecies) that remain or have been
eliminated. They focus instead on the success of recovery efforts for
wood bison ``ecotype,'' the increase in the number of animals, and the
establishment of new herds. We agree that significant strides have been
made towards recovery of wood bison, and we discussed the success of
recovery efforts in our proposed and final rules for the
reclassification of wood bison (76 FR 6734, 77 FR 26191). Although we
acknowledge that wood bison are no longer endangered, we conclude in
our final rule that threats to wood bison remain and that the wood
bison should be listed as threatened. In particular, we identified loss
of habitat, disease, and hybridization as ongoing threats. The
conclusions made in the May 3, 2012, final rule to reclassify the
subspecies are still valid. The petitioners have not provided, and we
have not received, any new information regarding threats to, or
recovery of, wood bison that was not considered in the final
reclassification rule.
[[Page 23536]]
Finding
The petition does not present substantial information to indicate
that delisting of wood bison is warranted. Although we recognize that
controversy exists around the subspecific designation for wood bison,
nomenclature stability, management history, and the acceptance of two
subspecies by the American Bison Specialist Group, the Canadian
National Wood Bison Recovery Team, and other zoologists lead us to the
conclusion that retaining the current nomenclature is appropriate and
defensible.
Although the petitioners argue that wood bison and plains bison
should be considered as one species, they did not indicate that all or
most threats to bison have been ameliorated. Instead, they focus on the
success of recovery efforts for wood bison. We agree that the status of
wood bison is more secure today than it once was. However, in our final
rule to reclassify wood bison as threatened, which published earlier
this year, we identified threats that remain to the species. The
petitioners did not provide any new information about the status of the
species that we were not already aware of and had evaluated in our
final rule.
On the basis of our determination under section 4(b)(3)(A) of the
Act, we conclude that the petition does not present substantial
scientific or commercial information to indicate that delisting the
wood bison under the Act may be warranted at this time. Although we
will not conduct a thorough review of the status of the species at this
time, we encourage interested parties to continue to gather data that
will assist with the conservation of the wood bison. If you wish to
provide information regarding the wood bison, you may submit your
information or materials to Marilyn Myers, Endangered Species
Biologist, Alaska Regional Office (see FOR FURTHER INFORMATION
CONTACT), at any time.
References Cited
A complete list of references cited is available on the Internet at
https://www.regulations.gov and upon request from the Alaska Regional
Office (see FOR FURTHER INFORMATION CONTACT).
Author
The primary author of this notice is Marilyn Myers of the Alaska
Regional Office (see FOR FURTHER INFORMATION CONTACT).
Authority
The authority for this action is the Endangered Species Act of
1973, as amended (16 U.S.C. 1531 et seq.).
Dated: November 7, 2012.
Daniel M. Ashe,
Director, U.S. Fish and Wildlife Service.
[FR Doc. 2013-09241 Filed 4-18-13; 8:45 am]
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