Endangered and Threatened Wildlife and Plants; Prudency Determination for the Designation of Critical Habitat for Trichostema austromontanum ssp. compactum, 56094-56098 [06-8190]
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56094
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Federal Register / Vol. 71, No. 186 / Tuesday, September 26, 2006 / Proposed Rules
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(4) Hand Delivery/Courier: You may
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(5) Federal Rulemaking Portal: https://
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FOR FURTHER INFORMATION CONTACT: Jim
Bartel, Field Supervisor, Carlsbad Fish
and Wildlife Office, telephone, 760/
431–9440; facsimile, 760/431–9624.
SUPPLEMENTARY INFORMATION:
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Dated: September 19, 2006.
David M. Verhey,
Acting Assistant Secretary for Fish and
Wildlife and Parks.
[FR Doc. 06–8191 Filed 9–25–06; 8:45 am]
BILLING CODE 4310–55–C
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
Public Comments Solicited
50 CFR Part 17
RIN 1018–AU77
Endangered and Threatened Wildlife
and Plants; Prudency Determination
for the Designation of Critical Habitat
for Trichostema austromontanum ssp.
compactum
Fish and Wildlife Service,
Interior.
ACTION: Notice of proposed finding.
AGENCY:
SUMMARY: We, the U.S. Fish and
Wildlife Service (Service), have
reconsidered whether designating
critical habitat for Trichostema
austromontanum ssp. compactum, a
plant, is prudent. This taxon was listed
as threatened under the Endangered
Species Act of 1973, as amended (Act),
on September 14, 1998; at that time we
determined that designation of critical
habitat was not prudent because
designation would increase the degree
of threat to the taxon and would not
benefit the taxon. As a consequence of
a settlement agreement we are
withdrawing our previous not prudent
finding. Further, on the basis of our
review and evaluation of the best
scientific and commercial information
available, we believe that designation of
critical habitat continues to be not
prudent for T. a. ssp. compactum. As a
result, we are proposing a new ‘‘not
prudent’’ determination for T. a. ssp.
compactum.
We will accept comments from
all interested parties until November 27,
2006.
ADDRESSES: If you wish to comment on
the proposed finding, you may submit
your comments and materials identified
by RIN 1018–AU77, by any of the
following methods:
(1) E-mail:
fw8cfwocomments@fws.gov. Include
‘‘RIN 1018–AU77’’ in the subject line.
(2) Fax: 760/431–9624.
(3) Mail: Jim Bartel, Field Supervisor,
Carlsbad Fish and Wildlife Office, 6010
Hidden Valley Road, Carlsbad, CA
92011.
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DATES:
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We intend that any final action
resulting from this finding will be as
accurate and as effective as possible.
Therefore, comments or suggestions
from the public, other concerned
governmental agencies, the scientific
community, industry, or any other
interested party concerning this
proposed finding are hereby solicited.
Comments particularly are sought
concerning:
(1) Reasons that designation of critical
habitat may or may not be prudent for
T. a. ssp. compactum;
(2) Specific information on
management activities for this taxon and
how those activities do or do not
address threats identified in the listing
rule;
(3) The possible risks and benefits of
designating critical habitat for T. a. ssp.
compactum; and
(4) Ways in which we could improve
or modify this finding to increase public
participation and understanding.
If you wish to comment, you may
submit your comments and materials
concerning this proposal by any one of
several methods (see ADDRESSES
section). Please submit Internet
comments to
fw8cfwocomments@fws.gov in ASCII file
format and avoid the use of special
characters or any form of encryption.
Please also include ‘‘Attn: RIN 1018–
AU77’’ in your e-mail subject header
and your name and return address in
the body of your message. If you do not
receive a confirmation from the system
that we have received your Internet
message, contact us directly by calling
our Carlsbad Fish and Wildlife Office at
phone number (760) 431–9440.
Our practice is to make comments,
including names and home addresses of
respondents, available for public review
during regular business hours.
Individual respondents may request that
we withhold their names and/or home
addresses, etc. but if you wish us to
consider withholding this information
you must state this prominently at the
beginning of your comments. In
addition, you must present rationale for
withholding this information. This
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rationale must demonstrate that
disclosure would constitute a clearly
unwarranted invasion of privacy.
Unsupported assertions will not meet
this burden. In the absence of
exceptional, documentable
circumstances, this information will be
released. We will always make
submissions from organizations or
businesses, and from individuals
identifying themselves as
representatives of or officials of
organizations or businesses, available
for public inspection in their entirety.
Comments and materials received will
be available for public inspection, by
appointment, during normal business
hours at the Carlsbad Fish and Wildlife
Office (see ADDRESSES).
Background
It is our intent to discuss only those
topics directly relevant to the not
prudent critical habitat determination.
For more information on biology and
ecology of Trichostema
austromontanum ssp. compactum, refer
to the final rule listing this taxon as
threatened published in the Federal
Register on September 14, 1998 (63 FR
49006).
Taxonomy and Description
Trichostema austromontanum ssp.
compactum, a member of the Lamiaceae
(mint family), was described by F.
Harlan Lewis (1945) based on
specimens collected in 1941 by M. L.
Hilend in Riverside County, California.
The taxon occurs only on the
northwestern margin of a single vernal
pool (Bauder 1999, p. 13). T. a. ssp.
compactum is a compact, soft-villous
(with long, shaggy hairs) annual plant,
approximately 4 inches (10 centimeters)
tall, with short internodes (stem
segments between leaves) (Lewis 1945,
p. 284–386, Lewis 1993, p. 732), elliptic
leaves, and blue flowers in a five-lobed
corolla. The two stamens are blue. The
fruit consists of four smooth, basally
joined nutlets. This taxon flowers in
July and August.
Threats
In the 1998 final listing rule, we
stated that trampling and low numbers
(small population size) threatened
Trichostema austromontanum ssp.
compactum (63 FR 49006). At the time
of listing there were reports of on-going
impacts caused by trampling associated
with hikers and horses. It was observed
that trampling by horses crushed plants
and also created depressions that
retained water where seeds and adult
plants of T. a. ssp. compactum drown
(Hamilton 1991, p 2, 22; Hamilton
1996). Since listing, the California
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Department of Parks and Recreation
(CDPR), which manages the area, has
taken several actions to minimize the
threat of trampling to this taxon (see the
‘‘Prudency Determination’’ section for a
detailed discussion).
Regarding the threat posed by low
numbers, the Service concluded in the
final listing rule that the limited number
of individual plants and the extremely
localized range of Trichostema
austromontanum ssp. compactum,
make this taxon more susceptible to
single disturbance events; such as
trampling during the flowering season
(63 FR 49006). According to Noss et al.
(1997), a species distributed across
multiple sites within its native range is
less susceptible to extinction than
another similar species confined to far
fewer sites. As a result, being restricted
to a single, small location clearly makes
the species more vulnerable to
stochastic (i.e., random, less
predictable) threats. Using the three
categories described by Noss et al.
(1997), these threats would be (1)
genetic (primarily loss of genetic
variation), (2) demographic (principally
extremely small population size), and
(3) environmental (vernal pool changes
and unknown stochastic events).
Previous Federal Actions
Trichostema austromontanum ssp.
compactum was federally listed as
threatened on September 14, 1998 (63
FR 49006). This taxon is not listed by
the State of California. At the time of
Federal listing, we determined that the
designation of critical habitat was not
prudent because the designation would
likely encourage more visitors to the
geographic location containing the
single known occurrence, and would
undermine attempts by the CDPR to
protect the site. We determined that
critical habitat designation would,
therefore, increase the degree of threat
to the taxon as well as provide no
benefit for the taxon. At the time of
listing, CDPR had initiated actions to
decrease the public notoriety of the
location and visibility of this taxon and
accessibility by the public to the
geographic location containing the
single occurrence in an effort to
decrease threats to this taxon. We
believed a critical habitat designation
would increase notoriety of the location
and visibility of the taxon, the opposite
of what the CDPR was trying to
accomplish. The increased notoriety
and visibility would potentially increase
visitorship to the area, thus increasing
the threat of trampling to the taxon.
On September 13, 2004, the Center for
Biological Diversity (CBD) and
California Native Plant Society (CNPS)
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challenged our failure to designate
critical habitat for this taxon and four
other plant species (Center for Biological
Diversity, et al. v. Gale Norton,
Secretary of the Department of the
Interior, et al., ED CV–04–1150 RT
(SGLx) C. D. California). The CBD and
CNPS alleged that the Service failed to
provide evidence in the final listing rule
supporting its finding that critical
habitat would not be beneficial to the
species and establishing how the
publication of critical habitat maps
would increase the threat to the species.
Without reaching any conclusions on
the merits of the previous decision, the
Service agreed to withdraw its previous
not prudent finding and publish a
proposed designation of critical habitat,
if prudent, on or before September 20,
2006, and a final rule by September 20,
2007. This withdrawal of the previous
not prudent finding and new proposed
prudency determination complies with
that settlement agreement.
Prudency Determination
Section 4(a)(3) of the Act and
implementing regulations (50 CFR
424.12) require that, to the maximum
extent prudent and determinable, we
designate critical habitat at the time a
species is determined to be endangered
or threatened. Regulations under 50 CFR
424.12(a)(1) state that the designation of
critical habitat is not prudent when one
or both of the following situations exist:
(1) The species is threatened by taking
or other activity and the identification
of critical habitat can be expected to
increase the degree of threat to the
species; or (2) such designation of
critical habitat would not be beneficial
to the species. In our September 14,
1998 final rule (63 FR 49006), we
determined that a designation of critical
habitat could increase the degree of
threat to Trichostema austromontanum
ssp. compactum, and that such
designation would also not be beneficial
to the taxon.
In the final listing rule (63 FR 49019)
we stated:
(1) Trichostema austromontanum ssp.
compactum occurs only in a wilderness
area on State [CDPR] lands with little
potential for Federal involvement.
Trails, signage, map notations, and
references to the habitat area have been
removed by the State to reduce impacts
to this highly localized taxon;
(2) Designation of critical habitat
would have little benefit to this taxon
and would not increase the commitment
or management efforts of the State; and
(3) Designation of critical habitat
likely would be detrimental to this
taxon because publishing maps and
descriptions of the exact locality
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identifies the site as a unique area. Such
a distinction may encourage recreational
use of the area and negatively impact
the taxon.
Pursuant to the Court’s April 14,
2005, stipulated settlement agreement
and order, we are hereby withdrawing
our previous ‘‘not prudent’’
determination. Consistent with the
requirements of the Act and our
aforementioned agreement and order,
we are simultaneously making a new
proposed determination of ‘‘not
prudent’’ for Trichostema
austromontanum ssp. compactum. An
explanation of this proposed ‘‘not
prudent’’ determination follows. We
encourage the public to comment on
this proposed determination as
described in the ‘‘Public Comments
Solicited’’ section above.
Trichostema austromontanum ssp.
compactum was listed based on threats
of trampling associated with
recreational activities and low numbers
of individual plants. Prior to the CDPR
taking steps to minimize the visibility of
the sensitive habitat that supports T. a.
ssp. compactum there was a clearly
marked trail to the location. The area
was used for many different types of
recreational uses. These activities
impacted the sensitive vegetation in the
area by trampling live plants and
creating multiple footprints in the wet
soil around the margin of the vernal
pool, further impacting habitat through
soil compaction and alteration of
hydrology (Hamilton 1983, 63 FR
49006). Since the taxon’s listing, the
CDPR has continued to implement
management actions designed to reduce
the visitation to this area. As stated in
the 1998 listing rule, they have removed
reference to the area from their trail
maps and signs, and removed all
markers for trails to this area in order to
reduce recreational use. Although the
taxon’s location was in the public
domain in the past, the exact location is
no longer easily accessible to the public
via normal information sources (e.g.,
internet). In contrast, the public notice
requirements of the Act, including
publication of site location information
and a map in the Federal Register, is
intended to make information readily
accessible to the public in a form that
is easy to understand.
The CDPR has continued their efforts
to address the threats from trampling by
further excluding recreational users
from the area. In 2000, CDPR erected a
barrier on the trail to the area to exclude
horses and pack animals from this
sensitive area. In 2002, they designated
the vernal pool and the surrounding
area as a Natural Preserve (CDPR 2002
p. 62). A Natural Preserve is a state
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designation that places resource
protection within the area over
recreational use and, therefore,
measures can be taken to ensure the
long-term survival of T. a. ssp.
compactum. Recent visits to the site
suggest that there has been a decrease in
equestrian use of the area as a result of
the barrier installed along the trail
(Wallace 2003, 2005; Snapp-Cook 2006).
As part of the process of determining
the prudency of designating critical
habitat for Trichostema
austromontanum ssp. compactum, we
met with CDPR to discuss management
activities now being conducted for this
taxon. The current and past actions that
they have initiated, partially due to the
listing of this taxon, appear to be
adequate to protect and maintain the
plant’s habitat. On a 2006 field visit to
the site, we only found signs of minimal
human use at the vernal pool reflected
in a worn trail passing the upper
boundary of the vernal pool; however,
we did not see evidence of higher
impact activities such as trash or fire
pits that would be associated with
camping, nor hoof prints or horse
manure that would be associated with
equestrian use (Snapp-Cook 2006). This
contrasted with the condition of the site
prior to the CDPR implementing
management actions for this plant and
the condition of the site described at the
time of listing (Hamilton 1983; 63 FR
49006). We were able to observe T. a.
ssp. compactum around the margins of
the vernal pool and none of the plants
showed any signs of damage from
trampling.
To support the effectiveness of the
management measures that CDPR has
put in place, a formal study to monitor
the recreation use of the area is needed.
The Service has recently helped the
State of California to secure funding to
conduct a study to determine the
condition of the population and the
effectiveness of the management by
CDPR. Funding has also been secured to
survey and sign the legal boundaries of
the established Natural Preserve so the
regulations of the Natural Preserve can
be enforced. In addition to these two
tasks, a seed banking program that
includes collection of seeds, a
conservation strategy, and monitoring,
will be established. Through this
funding, we are committed to work with
CDPR, California Department of Fish
and Game, the California Native Plant
Society and Rancho Santa Ana Botanic
Garden to establish a long-term
conservation strategy for T. a. ssp.
compactum. These actions should
provide additional protection for this
taxon and help to conserve this plant.
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While the primary threat to
Trichostema austromontanum ssp.
compactum, trampling, appears to have
been minimized, little information
exists on the status of the taxon overall.
To obtain all available information on
this taxon, we initiated a 5-year status
review. We published a notice
announcing the initiation of this review
for T. a. ssp. compactum and the
opening of the first 60-day comment
period in the Federal Register on July
7, 2005 (70 FR 39327). We published
another notice reopening the comment
period for an additional 60 days in the
Federal Register on November 3, 2005
(70 FR 66842). As part of our review, we
evaluated the federally-listed status of
this taxon based on the threats to the
plant and its habitat and recommended
that no change be made to the listing
status until a few specific conservation
actions underway by the CDPR have
been concluded. The completed 5-year
review for this taxon is available upon
request from the Field Supervisor,
Carlsbad Fish and Wildlife Office (see
ADDRESSES section).
Increased Threat to the Species
The process of designating critical
habitat would be expected to increase
human threats to Trichostema
austromontanum ssp. compactum by
bringing publicity to this plant and its
localized habitat with the publication of
maps likely resulting in an increase in
visitation to the site. We generally notify
all major regional newspapers, local,
State, and Federal agencies and other
interested parties, including all
Congressional offices in the local area
when designating critical habitat to raise
the visibility of our actions and involve
the public. These actions would
undermine the conservation efforts
taken by the CDPR to reduce the threat
of trampling to this taxon. For example,
the designation of critical habitat often
generates interest in a species and
inspires people to study the species and
visit the habitat. In the case of T. a. ssp.
compactum, it takes careful and
detailed training to recognize this taxon.
The plant is small and blends in with
other low-lying species on the ground.
It is unlikely that even informed hikers
could discern the plant’s presence in
particular areas. In addition, as
discussed above, this area has been
designated as a Natural Preserve, and
CDPR manages the area to minimize
recreational use. There are no signed
trails or observation areas in place that
could allow for interested persons to
observe the plant from a non-intrusive
location. Thus, even well-meaning and
informed visitors may cause significant
damage by inadvertently trampling
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these tiny plants and adversely affecting
the habitat.
The District Superintendent of the
Inland Empire District of California
State Parks has expressed concern to the
Service that the critical habitat
designation process may place this plant
at increased risk via increased visitation
(Watts 2006). Our publication of a
critical habitat map identifying the
location and subsequent publicity of
this action would be counter to CDPR’s
conservation actions to make the area
less visible. Prior to the CDPR taking
actions to minimize the recreational
impacts to this taxon, it was apparent
that the plant was in danger of going
extinct. The small size and delicate
structure of this plant make it especially
vulnerable to trampling by people and
animals (Lewis 1945, p. 284–386;
Hamilton 1996). The actions that CDPR
undertook once these concerns were
expressed began to reverse the negative
impacts to the taxon from recreational
activities. Following the listing of this
plant, CDPR continued to provide
measures that were designed to recover
it. It is important that these and further
conservation efforts continue so that
this taxon no longer requires the
protections afforded it under the Act.
We believe that the identification of the
specific areas essential to its
conservation, based on past experiences
and information concerning this taxon,
would be expected to further increase
the degree of threat to this plant from
human activity and undo the
conservation efforts and progress by
CDPR.
In addition to increasing threats to
this taxon and countering past and
ongoing conservation actions by the
State of California, designating critical
habitat for this plant would not support
our ongoing partnership with CDPR.
Most federally listed species in the
United States will not recover without
the cooperation of non-federal
landowners. Stein et al. (1995) found
that only about 12 percent of listed
species were found almost exclusively
on Federal lands (i.e., 90–100 percent of
their known occurrences restricted to
Federal lands) and that 50 percent of
federally listed species are not known to
occur on Federal lands at all. Given the
distribution of listed species with
respect to land ownership, conservation
of listed species in many parts of the
United States is dependent upon
working partnerships with a wide
variety of entities and the voluntary
cooperation of many non-federal
landowners (Wilcove and Chen 1998;
Crouse et al. 2002; James 2002).
Building partnerships and promoting
voluntary cooperation of landowners is
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essential to understanding the status of
species on non-federal lands and is
necessary to implement recovery actions
such as reintroducing listed species,
habitat restoration, and habitat
protection. Therefore, to achieve the
conservation of Trichostema
austromontanum ssp. compactum, it is
necessary to maintain our partnership
with CDPR.
Benefits to the Species From Critical
Habitat Designation
The most direct, and potentially
largest, regulatory benefit of critical
habitat is that federally authorized,
funded, or carried out activities require
consultation under section 7 of the Act
to ensure that they are not likely to
destroy or adversely modify critical
habitat. There are two limitations to this
regulatory effect. First, it only applies
where there is a Federal nexus—if there
is no Federal nexus, designation itself
does not restrict actions that destroy or
adversely modify critical habitat.
Second, it only limits destruction or
adverse modification. By its nature, the
prohibition on adverse modification is
designed to ensure those areas that
contain the physical and biological
features essential to the conservation of
the species or unoccupied areas that are
essential to the conservation of the
species are not eroded. Critical habitat
designation alone, however, does not
require specific steps toward recovery.
There is virtually no possibility of a
Federal nexus for activities that may
occur within Trichostema
austromontanum ssp. compactum’s
habitat. The San Jacinto Mountains have
been botanically explored for over 100
years and only one population of this
taxon has been found. Because of its
association with vernal pool margins,
other areas of suitable habitat likely do
not exist in this mountain range. The
Mount San Jacinto State Park
Wilderness is protected from uses that
would degrade or destroy natural
resources. The specific area where this
plant is found is designated as a Natural
Preserve, which means that protection
and management of sensitive resources
is the highest priority for this area. Due
to the fact that the taxon occurs only in
a Natural Preserve on State lands, an
area where no changes in land-use are
planned for the foreseeable future,
virtually no chance exists for a future
Federal nexus that would result in a
section 7 consultation for this taxon. In
fact, the Service has not engaged in any
consultations for T. a. ssp. compactum
since its listing in 1998.
Another benefit of including lands in
critical habitat is that the designation of
critical habitat serves to educate
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landowners, State and local
governments, and the public regarding
the potential conservation value of an
area. This helps focus and promote
conservation efforts by other parties by
clearly delineating areas of high
conservation value for the affected
species.
In this particular circumstance, any
educational benefits that could be
received through a designation of
critical habitat have the high probability
of undermining the conservation efforts
by CDPR and causing harm to
Trichostema austromontanum ssp.
compactum. The designation of critical
habitat often generates interest in a
species and inspires people to study the
species and visit the habitat. As
discussed above, T. a. ssp. compactum
is small and blends in with other lowlying species on the ground. Thus,
someone attempting to learn more about
this plant and its habitat would likely
actually harm members of the
population in the process.
The educational benefit is closely
related to a second, more indirect
benefit: that designation of critical
habitat informs State agencies and local
governments about areas that could be
conserved under State laws or local
ordinances. However, as discussed
above, CDPR is well aware of the areas
important to Trichostema
austromontanum ssp. compactum, and
is actively implementing measures to
conserve this taxon.
Increased Threat to the Species
Outweighs Benefits of Designation
Upon reviewing the available
information, we have determined that
the designation of critical habitat would
increase the degree of threat from
human activity to Trichostema
austromontanum ssp. compactum.
There is a strong possibility that through
the designation of critical habitat
negative impacts to the habitat would
occur. The dissemination of location
information is likely to result in an
increased threat to the plant from
trampling. Designation of critical habitat
will undermine the conservation actions
that CDPR has already put into place for
this taxon. These ongoing conservation
actions appear to have minimized the
primary threat to this taxon; and as
discussed above, we believe that
designation of critical habitat would
reverse these efforts and increase the
threat of trampling to this plant.
Furthermore, we have determined that
there is no benefit of critical habitat
designation to T. a. ssp. compactum
because (1) it is highly unlikely that a
Section 7 consultation will occur for
this taxon; (2) the general educational
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benefits afforded by critical habitat
designation are minimal for this
particular taxon; and (3) designation of
critical habitat would undermine
ongoing conservation efforts and hinder
our partnership with CDPR. Based on
our determination that critical habitat
designation would increase the degree
of threats to T. a. ssp. compactum and
our inability to determine a benefit of
designation, we believe the increased
threat to T. a. ssp. compactum from the
designation of critical habitat far
outweighs any benefits of designation.
Summary
Pursuant to the Court’s April 14,
2005, stipulated settlement agreement
and order we are withdrawing our
previous ‘‘not prudent’’ determination.
Further, on the basis of our review of
the best scientific and commercial
information available, we have
reaffirmed that designation of critical
habitat is not prudent for Trichostema
austromontanum ssp. compactum. We
have determined that the designation of
critical habitat would increase the
degree of threat to this taxon and will
undermine the conservation actions that
CDPR has already put into place for this
taxon. These ongoing conservation
actions appear to have minimized the
primary threat to T. a. ssp. compactum;
and as discussed above, we believe that
designation of critical habitat would
reverse these efforts and increase the
threat of trampling to this taxon.
Furthermore, we have determined that
there is no benefit of critical habitat
designation to T. a. ssp. compactum,
and that, even if some benefit from
designation may exist, the increased
threat to the plant from human activity
far outweighs any potential benefit to
the taxon. We therefore propose that it
is not prudent to designate critical
habitat for T. a. ssp. compactum at this
time.
Peer Review
In accordance with our joint policy
published in the Federal Register on
July 1, 1994 (59 FR 34270), and based
on our implementation of the Office of
Management and Budget (OMB) Final
Information Quality Bulletin for Peer
Review, dated December 16, 2004, we
will seek the expert opinions of at least
five appropriate and independent peer
reviewers regarding the science in this
proposed rule. The purpose of such
review is to ensure that our
determination is based on scientifically
sound data, assumptions, and analyses.
We will send copies of this proposed
determination to the peer reviewers
immediately following publication in
the Federal Register, and will invite the
E:\FR\FM\26SEP1.SGM
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56098
Federal Register / Vol. 71, No. 186 / Tuesday, September 26, 2006 / Proposed Rules
peer reviewers to comment during the
public comment period on the specific
assumptions and conclusions regarding
the proposed prudency determination.
We will consider all comments and
information received during the
comment period on this proposed
determination during preparation of a
final determination. Accordingly, the
final decision may differ from this
proposal.
Clarity of the Rule
Executive Order 12866 requires each
agency to write regulations and notices
that are easy to understand. We invite
your comments on how to make this
proposed determination easier to
understand, including answers to
questions such as the following: (1) Are
the requirements in the proposed
determination clearly stated? (2) Does
the document contain technical jargon
that interferes with the clarity? (3) Does
the format of the document (grouping
and order of the sections, use of
headings, paragraphing, and so forth)
aid or reduce its clarity? (4) Is the
description of the notice in the
SUPPLEMENTARY INFORMATION section
helpful in understanding the proposed
determination? (5) What else could we
do to make this proposed determination
easier to understand? Send a copy of
any comments on how we could make
this proposed determination easier to
understand to: Office of Regulatory
Affairs, Department of the Interior,
Room 7229, 1849 C Street, NW.,
Washington, DC 20240. You may e-mail
your comments to this address:
Exsec@ios.doi.gov.
sroberts on PROD1PC70 with PROPOSALS
Paperwork Reduction Act of 1995 (44
U.S.C. 3501 et seq.)
This proposed determination does not
contain any new collections of
information that require approval by
OMB under the Paperwork Reduction
Act. This determination will not impose
recordkeeping or reporting requirements
on State or local governments,
individuals, businesses, or
organizations. An agency may not
conduct or sponsor, and a person is not
required to respond to, a collection of
information unless it displays a
currently valid OMB control number.
on October 25, 1983 (48 FR 49244). This
assertion was upheld in the courts of the
Ninth Circuit (Douglas County v.
Babbitt, 48 F.3d 1495 (9th Cir. Ore.
1995), cert. denied 116 S. Ct. 698 (1996).
Government-to-Government
Relationship With Tribes
14:58 Sep 25, 2006
Jkt 208001
National Oceanic and Atmospheric
Administration
50 CFR Part 648
[Docket No. 060906236–6236–01; I.D.
083006B]
In accordance with the President’s
memorandum of April 29, 1994,
‘‘Government-to-Government Relations
with Native American Tribal
Governments’’ (59 FR 22951), Executive
Order 13175, and the Department of
Interior’s manual at 512 DM 2, we
readily acknowledge our responsibility
to communicate meaningfully with
recognized Federal tribes on a
government-to-government basis. We
have determined that there are no Tribal
lands occupied at the time of listing
contain the features essential for the
conservation and no tribal lands that are
unoccupied areas that are essential for
the conservation of Trichostema
austromontanum ssp. compactum.
Therefore, no tribal lands will be
affected by this finding.
RIN 0648–AU83
Fisheries of the Northeastern United
States; Method For Measuring Net
Mesh Size
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Proposed rule; request for
comments.
AGENCY:
The authority for this action is the
Endangered Species Act of 1973, as
amended (16 U.S.C. 1531 et seq.).
SUMMARY: NMFS proposes to amend the
regulations governing how fishing net
mesh size is measured in the Northeast.
This proposed change would increase
the weight used to measure mesh larger
than 120 mm (4.72 inches) in all
fisheries. The intent of this proposed
rule is to ensure consistent and accurate
measurements of fishing net mesh size.
DATES: Written comments must be
received no later than 5 p.m. local time
on October 26, 2006
ADDRESSES: Comments may be
submitted by any of the following
methods:
E-mail: MeshRegChange@noaa.gov
Federal e-Rulemaking Portal: https://
www.regulations.gov.
Mail: Patricia A. Kurkul, Regional
Administrator, Northeast Region,
National Marine Fisheries Service, One
Blackburn Drive, Gloucester, MA
01930–2298. Please write on the
envelope: Comments on Proposed
Change to Mesh Measurement
Regulations.
Dated: September 19, 2006.
David M. Verhey,
Acting Assistant Secretary for Fish and
Wildlife and Parks.
[FR Doc. 06–8190 Filed 9–25–06; 8:45 am]
FOR FURTHER INFORMATION CONTACT:
Douglas Potts, Fishery Management
Specialist, (978) 281–9341, FAX (978)
281–9135.
SUPPLEMENTARY INFORMATION:
BILLING CODE 4310–55–P
Background
References Cited
A complete list of all references cited
in this finding is available upon request
from the Field Supervisor, Carlsbad Fish
and Wildlife Office (see ADDRESSES
section).
Author
The primary author of this document
is staff of the Carlsbad Fish and Wildlife
Office (see ADDRESSES section).
Authority
NOAA Office of Law Enforcement,
U.S. Coast Guard, and state enforcement
partners have recently issued a
clarification of the method used in
measuring fishing net mesh size. This
protocol closely follows the regulatory
language, at 50 CFR Part 648, that a
wedge-shaped net measurement gauge
be allowed to settle under a specified
weight, without shaking the net or
pressing on the gauge to force it deeper
into the mesh opening. This
clarification eliminated some of the
National Environmental Policy Act
It is our position that, outside the
Tenth Circuit, we do not need to
prepare environmental analyses as
defined by the NEPA in connection with
designating critical habitat under the
Endangered Species Act of 1973, as
amended. We published a notice
outlining our reasons for this
determination in the Federal Register
VerDate Aug<31>2005
DEPARTMENT OF COMMERCE
PO 00000
Frm 00050
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Agencies
[Federal Register Volume 71, Number 186 (Tuesday, September 26, 2006)]
[Proposed Rules]
[Pages 56094-56098]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 06-8190]
-----------------------------------------------------------------------
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
RIN 1018-AU77
Endangered and Threatened Wildlife and Plants; Prudency
Determination for the Designation of Critical Habitat for Trichostema
austromontanum ssp. compactum
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Notice of proposed finding.
-----------------------------------------------------------------------
SUMMARY: We, the U.S. Fish and Wildlife Service (Service), have
reconsidered whether designating critical habitat for Trichostema
austromontanum ssp. compactum, a plant, is prudent. This taxon was
listed as threatened under the Endangered Species Act of 1973, as
amended (Act), on September 14, 1998; at that time we determined that
designation of critical habitat was not prudent because designation
would increase the degree of threat to the taxon and would not benefit
the taxon. As a consequence of a settlement agreement we are
withdrawing our previous not prudent finding. Further, on the basis of
our review and evaluation of the best scientific and commercial
information available, we believe that designation of critical habitat
continues to be not prudent for T. a. ssp. compactum. As a result, we
are proposing a new ``not prudent'' determination for T. a. ssp.
compactum.
DATES: We will accept comments from all interested parties until
November 27, 2006.
ADDRESSES: If you wish to comment on the proposed finding, you may
submit your comments and materials identified by RIN 1018-AU77, by any
of the following methods:
(1) E-mail: fw8cfwocomments@fws.gov. Include ``RIN 1018-AU77'' in
the subject line.
(2) Fax: 760/431-9624.
(3) Mail: Jim Bartel, Field Supervisor, Carlsbad Fish and Wildlife
Office, 6010 Hidden Valley Road, Carlsbad, CA 92011.
(4) Hand Delivery/Courier: You may hand-deliver written documents
to our office (see ADDRESSES).
(5) Federal Rulemaking Portal: https://www.regulations.gov. Follow
the instructions for submitting comments.
FOR FURTHER INFORMATION CONTACT: Jim Bartel, Field Supervisor, Carlsbad
Fish and Wildlife Office, telephone, 760/431-9440; facsimile, 760/431-
9624.
SUPPLEMENTARY INFORMATION:
Public Comments Solicited
We intend that any final action resulting from this finding will be
as accurate and as effective as possible. Therefore, comments or
suggestions from the public, other concerned governmental agencies, the
scientific community, industry, or any other interested party
concerning this proposed finding are hereby solicited. Comments
particularly are sought concerning:
(1) Reasons that designation of critical habitat may or may not be
prudent for T. a. ssp. compactum;
(2) Specific information on management activities for this taxon
and how those activities do or do not address threats identified in the
listing rule;
(3) The possible risks and benefits of designating critical habitat
for T. a. ssp. compactum; and
(4) Ways in which we could improve or modify this finding to
increase public participation and understanding.
If you wish to comment, you may submit your comments and materials
concerning this proposal by any one of several methods (see ADDRESSES
section). Please submit Internet comments to fw8cfwocomments@fws.gov in
ASCII file format and avoid the use of special characters or any form
of encryption. Please also include ``Attn: RIN 1018-AU77'' in your e-
mail subject header and your name and return address in the body of
your message. If you do not receive a confirmation from the system that
we have received your Internet message, contact us directly by calling
our Carlsbad Fish and Wildlife Office at phone number (760) 431-9440.
Our practice is to make comments, including names and home
addresses of respondents, available for public review during regular
business hours. Individual respondents may request that we withhold
their names and/or home addresses, etc. but if you wish us to consider
withholding this information you must state this prominently at the
beginning of your comments. In addition, you must present rationale for
withholding this information. This rationale must demonstrate that
disclosure would constitute a clearly unwarranted invasion of privacy.
Unsupported assertions will not meet this burden. In the absence of
exceptional, documentable circumstances, this information will be
released. We will always make submissions from organizations or
businesses, and from individuals identifying themselves as
representatives of or officials of organizations or businesses,
available for public inspection in their entirety. Comments and
materials received will be available for public inspection, by
appointment, during normal business hours at the Carlsbad Fish and
Wildlife Office (see ADDRESSES).
Background
It is our intent to discuss only those topics directly relevant to
the not prudent critical habitat determination. For more information on
biology and ecology of Trichostema austromontanum ssp. compactum, refer
to the final rule listing this taxon as threatened published in the
Federal Register on September 14, 1998 (63 FR 49006).
Taxonomy and Description
Trichostema austromontanum ssp. compactum, a member of the
Lamiaceae (mint family), was described by F. Harlan Lewis (1945) based
on specimens collected in 1941 by M. L. Hilend in Riverside County,
California. The taxon occurs only on the northwestern margin of a
single vernal pool (Bauder 1999, p. 13). T. a. ssp. compactum is a
compact, soft-villous (with long, shaggy hairs) annual plant,
approximately 4 inches (10 centimeters) tall, with short internodes
(stem segments between leaves) (Lewis 1945, p. 284-386, Lewis 1993, p.
732), elliptic leaves, and blue flowers in a five-lobed corolla. The
two stamens are blue. The fruit consists of four smooth, basally joined
nutlets. This taxon flowers in July and August.
Threats
In the 1998 final listing rule, we stated that trampling and low
numbers (small population size) threatened Trichostema austromontanum
ssp. compactum (63 FR 49006). At the time of listing there were reports
of on-going impacts caused by trampling associated with hikers and
horses. It was observed that trampling by horses crushed plants and
also created depressions that retained water where seeds and adult
plants of T. a. ssp. compactum drown (Hamilton 1991, p 2, 22; Hamilton
1996). Since listing, the California
[[Page 56095]]
Department of Parks and Recreation (CDPR), which manages the area, has
taken several actions to minimize the threat of trampling to this taxon
(see the ``Prudency Determination'' section for a detailed discussion).
Regarding the threat posed by low numbers, the Service concluded in
the final listing rule that the limited number of individual plants and
the extremely localized range of Trichostema austromontanum ssp.
compactum, make this taxon more susceptible to single disturbance
events; such as trampling during the flowering season (63 FR 49006).
According to Noss et al. (1997), a species distributed across multiple
sites within its native range is less susceptible to extinction than
another similar species confined to far fewer sites. As a result, being
restricted to a single, small location clearly makes the species more
vulnerable to stochastic (i.e., random, less predictable) threats.
Using the three categories described by Noss et al. (1997), these
threats would be (1) genetic (primarily loss of genetic variation), (2)
demographic (principally extremely small population size), and (3)
environmental (vernal pool changes and unknown stochastic events).
Previous Federal Actions
Trichostema austromontanum ssp. compactum was federally listed as
threatened on September 14, 1998 (63 FR 49006). This taxon is not
listed by the State of California. At the time of Federal listing, we
determined that the designation of critical habitat was not prudent
because the designation would likely encourage more visitors to the
geographic location containing the single known occurrence, and would
undermine attempts by the CDPR to protect the site. We determined that
critical habitat designation would, therefore, increase the degree of
threat to the taxon as well as provide no benefit for the taxon. At the
time of listing, CDPR had initiated actions to decrease the public
notoriety of the location and visibility of this taxon and
accessibility by the public to the geographic location containing the
single occurrence in an effort to decrease threats to this taxon. We
believed a critical habitat designation would increase notoriety of the
location and visibility of the taxon, the opposite of what the CDPR was
trying to accomplish. The increased notoriety and visibility would
potentially increase visitorship to the area, thus increasing the
threat of trampling to the taxon.
On September 13, 2004, the Center for Biological Diversity (CBD)
and California Native Plant Society (CNPS) challenged our failure to
designate critical habitat for this taxon and four other plant species
(Center for Biological Diversity, et al. v. Gale Norton, Secretary of
the Department of the Interior, et al., ED CV-04-1150 RT (SGLx) C. D.
California). The CBD and CNPS alleged that the Service failed to
provide evidence in the final listing rule supporting its finding that
critical habitat would not be beneficial to the species and
establishing how the publication of critical habitat maps would
increase the threat to the species. Without reaching any conclusions on
the merits of the previous decision, the Service agreed to withdraw its
previous not prudent finding and publish a proposed designation of
critical habitat, if prudent, on or before September 20, 2006, and a
final rule by September 20, 2007. This withdrawal of the previous not
prudent finding and new proposed prudency determination complies with
that settlement agreement.
Prudency Determination
Section 4(a)(3) of the Act and implementing regulations (50 CFR
424.12) require that, to the maximum extent prudent and determinable,
we designate critical habitat at the time a species is determined to be
endangered or threatened. Regulations under 50 CFR 424.12(a)(1) state
that the designation of critical habitat is not prudent when one or
both of the following situations exist: (1) The species is threatened
by taking or other activity and the identification of critical habitat
can be expected to increase the degree of threat to the species; or (2)
such designation of critical habitat would not be beneficial to the
species. In our September 14, 1998 final rule (63 FR 49006), we
determined that a designation of critical habitat could increase the
degree of threat to Trichostema austromontanum ssp. compactum, and that
such designation would also not be beneficial to the taxon.
In the final listing rule (63 FR 49019) we stated:
(1) Trichostema austromontanum ssp. compactum occurs only in a
wilderness area on State [CDPR] lands with little potential for Federal
involvement. Trails, signage, map notations, and references to the
habitat area have been removed by the State to reduce impacts to this
highly localized taxon;
(2) Designation of critical habitat would have little benefit to
this taxon and would not increase the commitment or management efforts
of the State; and
(3) Designation of critical habitat likely would be detrimental to
this taxon because publishing maps and descriptions of the exact
locality identifies the site as a unique area. Such a distinction may
encourage recreational use of the area and negatively impact the taxon.
Pursuant to the Court's April 14, 2005, stipulated settlement
agreement and order, we are hereby withdrawing our previous ``not
prudent'' determination. Consistent with the requirements of the Act
and our aforementioned agreement and order, we are simultaneously
making a new proposed determination of ``not prudent'' for Trichostema
austromontanum ssp. compactum. An explanation of this proposed ``not
prudent'' determination follows. We encourage the public to comment on
this proposed determination as described in the ``Public Comments
Solicited'' section above.
Trichostema austromontanum ssp. compactum was listed based on
threats of trampling associated with recreational activities and low
numbers of individual plants. Prior to the CDPR taking steps to
minimize the visibility of the sensitive habitat that supports T. a.
ssp. compactum there was a clearly marked trail to the location. The
area was used for many different types of recreational uses. These
activities impacted the sensitive vegetation in the area by trampling
live plants and creating multiple footprints in the wet soil around the
margin of the vernal pool, further impacting habitat through soil
compaction and alteration of hydrology (Hamilton 1983, 63 FR 49006).
Since the taxon's listing, the CDPR has continued to implement
management actions designed to reduce the visitation to this area. As
stated in the 1998 listing rule, they have removed reference to the
area from their trail maps and signs, and removed all markers for
trails to this area in order to reduce recreational use. Although the
taxon's location was in the public domain in the past, the exact
location is no longer easily accessible to the public via normal
information sources (e.g., internet). In contrast, the public notice
requirements of the Act, including publication of site location
information and a map in the Federal Register, is intended to make
information readily accessible to the public in a form that is easy to
understand.
The CDPR has continued their efforts to address the threats from
trampling by further excluding recreational users from the area. In
2000, CDPR erected a barrier on the trail to the area to exclude horses
and pack animals from this sensitive area. In 2002, they designated the
vernal pool and the surrounding area as a Natural Preserve (CDPR 2002
p. 62). A Natural Preserve is a state
[[Page 56096]]
designation that places resource protection within the area over
recreational use and, therefore, measures can be taken to ensure the
long-term survival of T. a. ssp. compactum. Recent visits to the site
suggest that there has been a decrease in equestrian use of the area as
a result of the barrier installed along the trail (Wallace 2003, 2005;
Snapp-Cook 2006).
As part of the process of determining the prudency of designating
critical habitat for Trichostema austromontanum ssp. compactum, we met
with CDPR to discuss management activities now being conducted for this
taxon. The current and past actions that they have initiated, partially
due to the listing of this taxon, appear to be adequate to protect and
maintain the plant's habitat. On a 2006 field visit to the site, we
only found signs of minimal human use at the vernal pool reflected in a
worn trail passing the upper boundary of the vernal pool; however, we
did not see evidence of higher impact activities such as trash or fire
pits that would be associated with camping, nor hoof prints or horse
manure that would be associated with equestrian use (Snapp-Cook 2006).
This contrasted with the condition of the site prior to the CDPR
implementing management actions for this plant and the condition of the
site described at the time of listing (Hamilton 1983; 63 FR 49006). We
were able to observe T. a. ssp. compactum around the margins of the
vernal pool and none of the plants showed any signs of damage from
trampling.
To support the effectiveness of the management measures that CDPR
has put in place, a formal study to monitor the recreation use of the
area is needed. The Service has recently helped the State of California
to secure funding to conduct a study to determine the condition of the
population and the effectiveness of the management by CDPR. Funding has
also been secured to survey and sign the legal boundaries of the
established Natural Preserve so the regulations of the Natural Preserve
can be enforced. In addition to these two tasks, a seed banking program
that includes collection of seeds, a conservation strategy, and
monitoring, will be established. Through this funding, we are committed
to work with CDPR, California Department of Fish and Game, the
California Native Plant Society and Rancho Santa Ana Botanic Garden to
establish a long-term conservation strategy for T. a. ssp. compactum.
These actions should provide additional protection for this taxon and
help to conserve this plant.
While the primary threat to Trichostema austromontanum ssp.
compactum, trampling, appears to have been minimized, little
information exists on the status of the taxon overall. To obtain all
available information on this taxon, we initiated a 5-year status
review. We published a notice announcing the initiation of this review
for T. a. ssp. compactum and the opening of the first 60-day comment
period in the Federal Register on July 7, 2005 (70 FR 39327). We
published another notice reopening the comment period for an additional
60 days in the Federal Register on November 3, 2005 (70 FR 66842). As
part of our review, we evaluated the federally-listed status of this
taxon based on the threats to the plant and its habitat and recommended
that no change be made to the listing status until a few specific
conservation actions underway by the CDPR have been concluded. The
completed 5-year review for this taxon is available upon request from
the Field Supervisor, Carlsbad Fish and Wildlife Office (see ADDRESSES
section).
Increased Threat to the Species
The process of designating critical habitat would be expected to
increase human threats to Trichostema austromontanum ssp. compactum by
bringing publicity to this plant and its localized habitat with the
publication of maps likely resulting in an increase in visitation to
the site. We generally notify all major regional newspapers, local,
State, and Federal agencies and other interested parties, including all
Congressional offices in the local area when designating critical
habitat to raise the visibility of our actions and involve the public.
These actions would undermine the conservation efforts taken by the
CDPR to reduce the threat of trampling to this taxon. For example, the
designation of critical habitat often generates interest in a species
and inspires people to study the species and visit the habitat. In the
case of T. a. ssp. compactum, it takes careful and detailed training to
recognize this taxon. The plant is small and blends in with other low-
lying species on the ground. It is unlikely that even informed hikers
could discern the plant's presence in particular areas. In addition, as
discussed above, this area has been designated as a Natural Preserve,
and CDPR manages the area to minimize recreational use. There are no
signed trails or observation areas in place that could allow for
interested persons to observe the plant from a non-intrusive location.
Thus, even well-meaning and informed visitors may cause significant
damage by inadvertently trampling these tiny plants and adversely
affecting the habitat.
The District Superintendent of the Inland Empire District of
California State Parks has expressed concern to the Service that the
critical habitat designation process may place this plant at increased
risk via increased visitation (Watts 2006). Our publication of a
critical habitat map identifying the location and subsequent publicity
of this action would be counter to CDPR's conservation actions to make
the area less visible. Prior to the CDPR taking actions to minimize the
recreational impacts to this taxon, it was apparent that the plant was
in danger of going extinct. The small size and delicate structure of
this plant make it especially vulnerable to trampling by people and
animals (Lewis 1945, p. 284-386; Hamilton 1996). The actions that CDPR
undertook once these concerns were expressed began to reverse the
negative impacts to the taxon from recreational activities. Following
the listing of this plant, CDPR continued to provide measures that were
designed to recover it. It is important that these and further
conservation efforts continue so that this taxon no longer requires the
protections afforded it under the Act. We believe that the
identification of the specific areas essential to its conservation,
based on past experiences and information concerning this taxon, would
be expected to further increase the degree of threat to this plant from
human activity and undo the conservation efforts and progress by CDPR.
In addition to increasing threats to this taxon and countering past
and ongoing conservation actions by the State of California,
designating critical habitat for this plant would not support our
ongoing partnership with CDPR.
Most federally listed species in the United States will not recover
without the cooperation of non-federal landowners. Stein et al. (1995)
found that only about 12 percent of listed species were found almost
exclusively on Federal lands (i.e., 90-100 percent of their known
occurrences restricted to Federal lands) and that 50 percent of
federally listed species are not known to occur on Federal lands at
all. Given the distribution of listed species with respect to land
ownership, conservation of listed species in many parts of the United
States is dependent upon working partnerships with a wide variety of
entities and the voluntary cooperation of many non-federal landowners
(Wilcove and Chen 1998; Crouse et al. 2002; James 2002). Building
partnerships and promoting voluntary cooperation of landowners is
[[Page 56097]]
essential to understanding the status of species on non-federal lands
and is necessary to implement recovery actions such as reintroducing
listed species, habitat restoration, and habitat protection. Therefore,
to achieve the conservation of Trichostema austromontanum ssp.
compactum, it is necessary to maintain our partnership with CDPR.
Benefits to the Species From Critical Habitat Designation
The most direct, and potentially largest, regulatory benefit of
critical habitat is that federally authorized, funded, or carried out
activities require consultation under section 7 of the Act to ensure
that they are not likely to destroy or adversely modify critical
habitat. There are two limitations to this regulatory effect. First, it
only applies where there is a Federal nexus--if there is no Federal
nexus, designation itself does not restrict actions that destroy or
adversely modify critical habitat. Second, it only limits destruction
or adverse modification. By its nature, the prohibition on adverse
modification is designed to ensure those areas that contain the
physical and biological features essential to the conservation of the
species or unoccupied areas that are essential to the conservation of
the species are not eroded. Critical habitat designation alone,
however, does not require specific steps toward recovery.
There is virtually no possibility of a Federal nexus for activities
that may occur within Trichostema austromontanum ssp. compactum's
habitat. The San Jacinto Mountains have been botanically explored for
over 100 years and only one population of this taxon has been found.
Because of its association with vernal pool margins, other areas of
suitable habitat likely do not exist in this mountain range. The Mount
San Jacinto State Park Wilderness is protected from uses that would
degrade or destroy natural resources. The specific area where this
plant is found is designated as a Natural Preserve, which means that
protection and management of sensitive resources is the highest
priority for this area. Due to the fact that the taxon occurs only in a
Natural Preserve on State lands, an area where no changes in land-use
are planned for the foreseeable future, virtually no chance exists for
a future Federal nexus that would result in a section 7 consultation
for this taxon. In fact, the Service has not engaged in any
consultations for T. a. ssp. compactum since its listing in 1998.
Another benefit of including lands in critical habitat is that the
designation of critical habitat serves to educate landowners, State and
local governments, and the public regarding the potential conservation
value of an area. This helps focus and promote conservation efforts by
other parties by clearly delineating areas of high conservation value
for the affected species.
In this particular circumstance, any educational benefits that
could be received through a designation of critical habitat have the
high probability of undermining the conservation efforts by CDPR and
causing harm to Trichostema austromontanum ssp. compactum. The
designation of critical habitat often generates interest in a species
and inspires people to study the species and visit the habitat. As
discussed above, T. a. ssp. compactum is small and blends in with other
low-lying species on the ground. Thus, someone attempting to learn more
about this plant and its habitat would likely actually harm members of
the population in the process.
The educational benefit is closely related to a second, more
indirect benefit: that designation of critical habitat informs State
agencies and local governments about areas that could be conserved
under State laws or local ordinances. However, as discussed above, CDPR
is well aware of the areas important to Trichostema austromontanum ssp.
compactum, and is actively implementing measures to conserve this
taxon.
Increased Threat to the Species Outweighs Benefits of Designation
Upon reviewing the available information, we have determined that
the designation of critical habitat would increase the degree of threat
from human activity to Trichostema austromontanum ssp. compactum. There
is a strong possibility that through the designation of critical
habitat negative impacts to the habitat would occur. The dissemination
of location information is likely to result in an increased threat to
the plant from trampling. Designation of critical habitat will
undermine the conservation actions that CDPR has already put into place
for this taxon. These ongoing conservation actions appear to have
minimized the primary threat to this taxon; and as discussed above, we
believe that designation of critical habitat would reverse these
efforts and increase the threat of trampling to this plant.
Furthermore, we have determined that there is no benefit of critical
habitat designation to T. a. ssp. compactum because (1) it is highly
unlikely that a Section 7 consultation will occur for this taxon; (2)
the general educational benefits afforded by critical habitat
designation are minimal for this particular taxon; and (3) designation
of critical habitat would undermine ongoing conservation efforts and
hinder our partnership with CDPR. Based on our determination that
critical habitat designation would increase the degree of threats to T.
a. ssp. compactum and our inability to determine a benefit of
designation, we believe the increased threat to T. a. ssp. compactum
from the designation of critical habitat far outweighs any benefits of
designation.
Summary
Pursuant to the Court's April 14, 2005, stipulated settlement
agreement and order we are withdrawing our previous ``not prudent''
determination. Further, on the basis of our review of the best
scientific and commercial information available, we have reaffirmed
that designation of critical habitat is not prudent for Trichostema
austromontanum ssp. compactum. We have determined that the designation
of critical habitat would increase the degree of threat to this taxon
and will undermine the conservation actions that CDPR has already put
into place for this taxon. These ongoing conservation actions appear to
have minimized the primary threat to T. a. ssp. compactum; and as
discussed above, we believe that designation of critical habitat would
reverse these efforts and increase the threat of trampling to this
taxon. Furthermore, we have determined that there is no benefit of
critical habitat designation to T. a. ssp. compactum, and that, even if
some benefit from designation may exist, the increased threat to the
plant from human activity far outweighs any potential benefit to the
taxon. We therefore propose that it is not prudent to designate
critical habitat for T. a. ssp. compactum at this time.
Peer Review
In accordance with our joint policy published in the Federal
Register on July 1, 1994 (59 FR 34270), and based on our implementation
of the Office of Management and Budget (OMB) Final Information Quality
Bulletin for Peer Review, dated December 16, 2004, we will seek the
expert opinions of at least five appropriate and independent peer
reviewers regarding the science in this proposed rule. The purpose of
such review is to ensure that our determination is based on
scientifically sound data, assumptions, and analyses. We will send
copies of this proposed determination to the peer reviewers immediately
following publication in the Federal Register, and will invite the
[[Page 56098]]
peer reviewers to comment during the public comment period on the
specific assumptions and conclusions regarding the proposed prudency
determination. We will consider all comments and information received
during the comment period on this proposed determination during
preparation of a final determination. Accordingly, the final decision
may differ from this proposal.
Clarity of the Rule
Executive Order 12866 requires each agency to write regulations and
notices that are easy to understand. We invite your comments on how to
make this proposed determination easier to understand, including
answers to questions such as the following: (1) Are the requirements in
the proposed determination clearly stated? (2) Does the document
contain technical jargon that interferes with the clarity? (3) Does the
format of the document (grouping and order of the sections, use of
headings, paragraphing, and so forth) aid or reduce its clarity? (4) Is
the description of the notice in the SUPPLEMENTARY INFORMATION section
helpful in understanding the proposed determination? (5) What else
could we do to make this proposed determination easier to understand?
Send a copy of any comments on how we could make this proposed
determination easier to understand to: Office of Regulatory Affairs,
Department of the Interior, Room 7229, 1849 C Street, NW., Washington,
DC 20240. You may e-mail your comments to this address:
Exsec@ios.doi.gov.
Paperwork Reduction Act of 1995 (44 U.S.C. 3501 et seq.)
This proposed determination does not contain any new collections of
information that require approval by OMB under the Paperwork Reduction
Act. This determination will not impose recordkeeping or reporting
requirements on State or local governments, individuals, businesses, or
organizations. An agency may not conduct or sponsor, and a person is
not required to respond to, a collection of information unless it
displays a currently valid OMB control number.
National Environmental Policy Act
It is our position that, outside the Tenth Circuit, we do not need
to prepare environmental analyses as defined by the NEPA in connection
with designating critical habitat under the Endangered Species Act of
1973, as amended. We published a notice outlining our reasons for this
determination in the Federal Register on October 25, 1983 (48 FR
49244). This assertion was upheld in the courts of the Ninth Circuit
(Douglas County v. Babbitt, 48 F.3d 1495 (9th Cir. Ore. 1995), cert.
denied 116 S. Ct. 698 (1996).
Government-to-Government Relationship With Tribes
In accordance with the President's memorandum of April 29, 1994,
``Government-to-Government Relations with Native American Tribal
Governments'' (59 FR 22951), Executive Order 13175, and the Department
of Interior's manual at 512 DM 2, we readily acknowledge our
responsibility to communicate meaningfully with recognized Federal
tribes on a government-to-government basis. We have determined that
there are no Tribal lands occupied at the time of listing contain the
features essential for the conservation and no tribal lands that are
unoccupied areas that are essential for the conservation of Trichostema
austromontanum ssp. compactum. Therefore, no tribal lands will be
affected by this finding.
References Cited
A complete list of all references cited in this finding is
available upon request from the Field Supervisor, Carlsbad Fish and
Wildlife Office (see ADDRESSES section).
Author
The primary author of this document is staff of the Carlsbad Fish
and Wildlife Office (see ADDRESSES section).
Authority
The authority for this action is the Endangered Species Act of
1973, as amended (16 U.S.C. 1531 et seq.).
Dated: September 19, 2006.
David M. Verhey,
Acting Assistant Secretary for Fish and Wildlife and Parks.
[FR Doc. 06-8190 Filed 9-25-06; 8:45 am]
BILLING CODE 4310-55-P