Endangered and Threatened Wildlife and Plants; Designation of Critical Habitat for Acanthomintha ilicifolia, 11946-11988 [07-1100]
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hours at the Carlsbad Fish and Wildlife
Office at the above address (telephone
760–431–9440).
FOR FURTHER INFORMATION CONTACT: Jim
Bartel, Field Supervisor, Carlsbad Fish
and Wildlife Office at the address or
telephone number listed under
ADDRESSES. Persons who use a
telecommunications device for the deaf
(TDD) may call the Federal Information
Relay Service (FIRS) at 800–877–8339.
SUPPLEMENTARY INFORMATION:
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
RIN 1018–AU86
Endangered and Threatened Wildlife
and Plants; Designation of Critical
Habitat for Acanthomintha ilicifolia
(San Diego thornmint)
Fish and Wildlife Service,
Interior.
ACTION: Proposed rule.
AGENCY:
Public Comments Solicited
We, the U.S. Fish and
Wildlife Service (Service), propose to
designate critical habitat for
Acanthomintha ilicifolia (San Diego
thornmint) under the Endangered
Species Act of 1973, as amended (Act).
We have determined that a total of
approximately 1,936 acres (ac) (783
hectares (ha)) in San Diego County,
California, meets the definition of
critical habitat. We are proposing to
exclude 1,302 ac (527 ha) from the
critical habitat designation. If these
proposed exclusions are adopted, this
would result in a designation of critical
habitat of approximately 634 ac (257 ha)
of land under Federal (553 ac (224 ha)),
and State and local (81 ac (33 ha)),
ownership in San Diego County,
California.
SUMMARY:
We will accept comments from
all interested parties until May 14, 2007.
We must receive requests for public
hearings, in writing, at the address
shown in the ADDRESSES section by
April 30, 2007.
ADDRESSES: If you wish to comment on
the proposed rule, you may submit your
comments and materials identified by
RIN 1018–AU86, by any of the following
methods:
(1) You may send comments by
electronic mail (e-mail) to
fw8cfwocomments@fws.gov. Include
‘‘RIN 1018–AU86’’ in the subject line.
(2) You may fax your comments to Jim
Bartel, Field Supervisor, Carlsbad Fish
and Wildlife Office at 760–431–5901.
(3) You may mail or hand-deliver
your written comments and information
to Jim Bartel, Field Supervisor, Carlsbad
Fish and Wildlife Office, 6010 Hidden
Valley Road, Carlsbad, CA 92011.
(4) You may submit your comments at
the Federal eRulemaking Portal, https://
www.regulations.gov. Follow the
instructions for submitting comments.
Comments and materials received, as
well as supporting documentation used
in the preparation of this proposed rule,
will be available for public inspection,
by appointment, during normal business
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DATES:
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We intend that any final action
resulting from this proposal 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 rule are hereby solicited.
Comments particularly are sought
concerning:
(1) The reasons any habitat should or
should not be determined to be critical
habitat as provided by section 4 of the
Act, including whether the benefit of
designation will outweigh any threats to
the species due to designation;
(2) Specific information on the
amount and distribution of
Acanthomintha ilicifolia habitat and
what areas should be included in the
designation that were occupied at the
time of listing that contain the features
essential for the conservation of the
species, and why and what areas that
were not occupied at the time of listing
are essential to the conservation of the
species;
(3) Land use designations and current
or planned activities in the subject areas
and their possible impacts on proposed
critical habitat;
(4) Our proposed exclusion of 1,302
acres (ac) (527 hectares (ha)) of nonFederal lands already conserved or
targeted for conservation within subarea
plans under the San Diego Multiple
Species Conservation Program (MSCP)
and the San Diego Multiple Habitat
Conservation Program (MHCP) from the
final designation of critical habitat for
Acanthomintha ilicifolia under section
4(b)(2) of the Act. We are specifically
seeking public comment on our
proposed exclusion of lands covered
under the City of Encinitas subarea plan
of the MHCP (see Exclusions Under
Section 4(b)(2) of the Act for details of
these HCPs). It is our understanding that
little progress has been made by the City
of Encinitas to finalize their subarea
plan since the 2001 release of the draft
plan. Based on information received
during the public comment period, the
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Secretary may determine that sufficient
progress has not been made and that
lands within the City of Encinitas’
subarea plan should not be excluded
from the final designation. Specifically,
useful information would include:
Whether essential lands within
Encinitas are being managed, or are
proposed to be managed, to conserve A.
ilicifolia, and; the outlook for
completion of the draft subarea plan.
Please provide information concerning
whether the benefits of exclusion of any
of these specific areas outweigh the
benefits of their inclusion in designated
critical habitat. If the Secretary
determines the benefits of including
these lands outweigh the benefits of
excluding them, they will not be
excluded from final critical habitat;
(5) Any foreseeable economic,
national security, or other potential
impacts resulting from the proposed
designation and, in particular, any
impacts on small entities; and
(6) Whether our approach to
designating critical habitat could be
improved or modified in any way to
provide for greater public participation
and understanding, or to assist us in
accommodating public concerns and
comments.
If you wish to comment, you may
submit your comments and materials
concerning this proposal by any one of
several methods (see ADDRESSES). Please
submit e-mail comments to
fw8cfwocomments@fws.gov. Please also
include ‘‘Attn: RIN 1018–AU86’’ in your
e-mail subject line 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 message, contact us
directly by calling our Carlsbad Fish
and Wildlife Office at phone number
760–431–9440. Please note that
comments must be received by the date
specified in DATES in order to be
considered.
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 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
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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.
Role of Critical Habitat in Actual
Practice of Administering and
Implementing the Act
Attention to and protection of habitat
is paramount to successful conservation
actions. The role that designation of
critical habitat plays in protecting
habitat of listed species, however, is
often misunderstood. As discussed in
more detail below in the discussion of
exclusions under section 4(b)(2) of the
Act, there are significant limitations on
the regulatory effect of designation
under section 7(a)(2) of the Act. In brief,
(1) designation provides additional
protection to habitat only where there is
a Federal nexus; (2) the protection is
relevant only when, in the absence of
designation, destruction or adverse
modification of the critical habitat
would in fact take place (in other words,
other statutory or regulatory protections,
policies, or other factors relevant to
agency decision-making would not
prevent the destruction or adverse
modification); and (3) designation of
critical habitat triggers the prohibition
of destruction or adverse modification
of that habitat, but it does not require
specific actions to restore or improve
habitat.
Currently, only 483 species, or 37
percent of the 1,311 listed species in the
United States under the jurisdiction of
the Service have designated critical
habitat. We address the habitat needs of
listed species through conservation
mechanisms such as listing, section 7
consultations, the section 4 recovery
planning process, the section 9
protective prohibitions of unauthorized
take, section 6 funding to the States, the
section 10 incidental take permit
process and cooperative, nonregulatory
efforts with private landowners. The
Service believes that it is these measures
that may make the difference between
extinction and survival for many
species.
In considering exclusions of areas
proposed for designation, we evaluate
the benefits of designation in light of
Gifford Pinchot Task Force v. U.S. Fish
and Wildlife Service, 378 F.3d 1059 (9th
Cir. 2004) (hereinafter Gifford Pinchot).
In that case, the Ninth Circuit
invalidated the Service’s regulation
defining ‘‘destruction or adverse
modification of critical habitat.’’ In
response, on December 9, 2004, the
Director issued guidance to be
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considered in making section 7 adverse
modification determinations. This
proposed critical habitat designation
does not use the invalidated regulation
in our consideration of the benefits of
including areas in the proposed
designation. The Service will carefully
manage future consultations that
analyze impacts to designated critical
habitat, particularly those that appear to
be resulting in an adverse modification
determination. Such consultations will
be reviewed by the Regional Office prior
to finalizing to ensure that an adequate
analysis has been conducted that is
informed by the Director’s guidance.
On the other hand, to the extent that
designation of critical habitat provides
protection, that protection can come at
significant social and economic cost. In
addition, the mere administrative
process of designation of critical habitat
is expensive, time-consuming, and
controversial. The current statutory
framework of critical habitat, combined
with past judicial interpretations of the
statute, make critical habitat the subject
of excessive litigation. As a result,
critical habitat designations are driven
by litigation and courts rather than
biology, and made at a time and under
a timeframe that limits our ability to
obtain and evaluate the scientific and
other information required to make the
designation most meaningful.
In light of these circumstances, the
Service believes that additional agency
discretion would allow our focus to
return to those actions that provide the
greatest benefit to the species most in
need of protection.
Procedural and Resource Difficulties in
Designating Critical Habitat
We have been inundated with
lawsuits for our failure to designate
critical habitat, and we face a growing
number of lawsuits challenging critical
habitat determinations once they are
made. These lawsuits have subjected the
Service to an ever-increasing series of
court orders and court-approved
settlement agreements, compliance with
which now consumes nearly the entire
listing program budget. This leaves the
Service with little ability to prioritize its
activities to direct scarce listing
resources to the listing program actions
with the most biologically urgent
species conservation needs.
The consequence of the critical
habitat litigation activity is that limited
listing funds are used to defend active
lawsuits, to respond to Notices of Intent
to sue relative to critical habitat, and to
comply with the growing number of
adverse court orders. As a result, listing
petition responses, the Service’s own
proposals to list critically imperiled
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species, and final listing determinations
on existing proposals are all
significantly delayed.
The accelerated schedules of courtordered designations have left the
Service with limited ability to provide
for public participation or to ensure a
defect-free rulemaking process before
making decisions on listing and critical
habitat proposals, due to the risks
associated with noncompliance with
judicially imposed deadlines. This in
turn fosters a second round of litigation
in which those who fear adverse
impacts from critical habitat
designations challenge those
designations. The cycle of litigation
appears endless, and is very expensive,
thus diverting resources from
conservation actions that may provide
relatively more benefit to imperiled
species.
The costs resulting from the
designation include legal costs, the cost
of preparation and publication of the
designation, the analysis of the
economic effects and the cost of
requesting and responding to public
comment, and in some cases the costs
of compliance with the National
Environmental Policy Act (NEPA) (42
U.S.C. 4321 et seq.). These costs, which
are not required for many other
conservation actions, directly reduce the
funds available for direct and tangible
conservation actions.
Background
It is our intent to discuss only those
topics directly relevant to the
designation of critical habitat in this
proposed rule. For more information on
the biology and ecology of
Acanthomintha ilicifolia, please refer to
the final rule listing the species as
threatened published in the Federal
Register on October 13, 1998 (63 FR
54938). This species has been listed by
the State of California as endangered
since 1982.
Species Description and Life History
Acanthomintha ilicifolia (San Diego
thornmint) is an annual member of the
mint family in the genus
Acanthomintha. This plant ranges in
height from 2 to 6 inches (in) (5 to 15
centimeters (cm)) and has white, twolipped, tubular flowers with rosecolored markings on the lower lip
(Jokerst 1993, p. 713). Members of this
genus have paired leaves and several
sharp spiny bracts (modified leaves)
below whorled flowers. Acanthomintha
ilicifolia can be distinguished from
other members of the genus by its
flower, which has hairless anthers and
style.
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Distribution, Ecology, and Habitat
Acanthomintha ilicifolia usually
occurs on heavy clay soils in open areas
surrounded by shrubby vegetation.
These openings are generally found
within coastal sage scrub, chaparral and
native grassland of coastal San Diego
County and south to San Telmo in
northern Baja California, Mexico
(Beauchamp 1986, p. 175; Reiser 2001,
pp. 3–5). Acanthomintha ilicifolia is
frequently associated with gabbro soils,
which are derived from igneous rock,
and gray calcareous clays derived from
soft calcareous sandstone (Oberbauer
and Vanderwier 1991, pp. 208–209).
This species is endemic to San Diego
County, California, and northwestern
Baja California, Mexico, and grows on
open clay lenses described as friable,
meaning that these soils have a loose,
crumbly texture.
In the final listing rule for
Acanthomintha ilicifolia (63 FR 54938,
October 13, 1998), 32 of 52 historic
populations were presumed to be extant
(still in existence). In the listing rule we
estimated that the total number of
individual plants in all remaining
populations was approximately 150,000
to 170,000 (63 FR 54938). Throughout
this proposed rule, occurrences of A.
ilicifolia are referred to by their element
occurrence (EO) number. This is a code
that is assigned to each specific location
of rare species that is cataloged in the
California Natural Diversity Database
(CNDDB). Element occurrences do not
necessarily represent populations, but
are used to represent areas where a
species is found. Element occurrences
that are close together may be part of the
same population. Therefore, the number
of element occurrences does not
represent the number of populations
that exist for this species. For the
purpose of this proposed critical habitat
designation, we are assuming that
element occurrences within one mile
(1.6 kilometers (km)) of each other and
on habitat that is not fragmented by
roads or structures are part of the same
population.
Through surveys associated with the
development of Habitat Conservation
Plans (HCPs) and additional surveys on
public and private lands since the time
of listing, additional populations of A.
ilicifolia have been discovered. We
currently have data for a total of 88
element occurrences (or 64 populations)
of which 54 element occurrences (or 34
populations) are extant or presumed
extant and 34 element occurrences (or
30 populations) are considered to be
extirpated (no longer in existence) or
possibly extirpated. Specifically, we
consider 68 element occurrences to have
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been known at the time of listing in
1998 (52 historic populations) and an
additional 20 element occurrences to
have been discovered since the time of
listing (12 new populations). Detailed
information about the new element
occurrences is available upon request
from the Carlsbad Fish and Wildlife
Office (see ADDRESSES).
Previous Federal Actions
Acanthomintha ilicifolia was
federally listed as threatened on October
13, 1998 (63 FR 54938), and has been
listed as endangered by the State of
California since 1982 (CDFG 2006, p.1).
This species currently does not have a
recovery plan.
At the time this plant was federally
listed, the Service compared the benefits
of designating critical habitat to the
detrimental effects (threats) of increased
collection and vandalism and the
potential for private landowner
misunderstandings about the effects of
critical habitat designation on private
lands (63 FR 54938, pp. 54951–54953).
Additionally, we conflated the jeopardy
standard with the standard for
destruction or adverse modification of
critical habitat, stating that a jeopardy
finding would be equivalent to a finding
of adverse modification of critical
habitat thereby resulting in identical
section 7 findings. Based on these
factors, the Service found that
designation of critical habitat for A.
ilicifolia was not prudent.
On August 10, 2004, the Center for
Biological Diversity and California
Native Plant Society challenged our
failure to designate critical habitat for
this species as well as four other plant
species (Center for Biological Diversity
v. Norton, C–04–3240 JL (N. D. Cal.)). In
settlement of the lawsuit, the Service
agreed to withdraw our previous not
prudent finding and deliver a proposed
determination of critical habitat, if
prudent, to the Federal Register on or
before February 28, 2007 and a final
designation by February 28, 2008.
We have re-evaluated the prudency of
designating critical habitat for this
species. Despite the potential threats to
this species from collection and
vandalism and the continuing potential
for private landowner
misunderstandings about the effects of
critical habitat designation on private
land, we believe that designation of
critical habitat will benefit A. ilicifolia.
As a result of the Gifford Pinchot court
ruling in 2004, we now recognize the
jeopardy standard and the standard for
destruction or adverse modification of
critical habitat are separate and distinct.
Additionally, we recognize critical
habitat designations may provide
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benefits to the recovery of a species.
Therefore, we now find designation of
critical habitat for A. ilicifolia to be
prudent because designation of critical
habitat has the potential to provide
greater protections to the species and its
habitat than the jeopardy standard
under section 7(a)(2) of the Act.
Critical Habitat
Critical habitat is defined in section 3
of the Act as—(i) the specific areas
within the geographical area occupied
by a species, at the time it is listed in
accordance with the Act, on which are
found those physical or biological
features (I) essential to the conservation
of the species and (II) that may require
special management considerations or
protection; and (ii) specific areas
outside the geographical area occupied
by a species at the time it is listed, upon
a determination that such areas are
essential for the conservation of the
species. Conservation, as defined under
section 3 of the Act, means to use and
the use of all methods and procedures
which are necessary to bring any
endangered species or threatened
species to the point at which the
measures provided pursuant to the Act
are no longer necessary. Such methods
and procedures include, but are not
limited to, all activities associated with
scientific resources management such as
research, census, law enforcement,
habitat acquisition and maintenance,
propagation, live trapping, and
transplantation, and, in the
extraordinary case where population
pressures within a given ecosystem
cannot be otherwise relieved, may
include regulated taking.
Critical habitat receives protection
under section 7 of the Act through the
prohibition against destruction or
adverse modification of critical habitat
with regard to actions carried out,
funded, or authorized by a Federal
agency. Section 7 of the Act requires
consultation on Federal actions that are
likely to result in the destruction or
adverse modification of critical habitat.
The designation of critical habitat does
not affect land ownership or establish a
refuge, wilderness, reserve, preserve, or
other conservation area. Such
designation does not allow government
or public access to private lands.
Section 7 of the Act is a purely
protective measure and does not require
implementation of restoration, recovery,
or enhancement measures.
To be included in a critical habitat
designation, the habitat within the area
occupied by the species must first have
features that are essential to the
conservation of the species. Critical
habitat designations identify, to the
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extent known using the best scientific
data available, habitat areas that provide
essential life cycle needs of the species
(i.e., areas on which are found the
primary constituent elements, as
defined at 50 CFR 424.12(b)). Habitat
within the geographic area occupied by
the species at the time of listing may be
included in critical habitat only if the
essential features thereon may require
special management considerations or
protection. Areas outside of the
geographic area occupied by the species
at the time of listing may only be
included in critical habitat if they are
essential for the conservation of the
species. Accordingly, when the best
available scientific data do not
demonstrate that the conservation needs
of the species require additional areas,
we will not designate critical habitat in
areas outside the geographical area
occupied by the species at the time of
listing. An area currently occupied by
the species but not known to be
occupied at the time of listing will
likely, but not always, be essential to the
conservation of the species and,
therefore, typically included in the
critical habitat designation.
The Service’s Policy on Information
Standards Under the Endangered
Species Act, published in the Federal
Register on July 1, 1994 (59 FR 34271),
and Section 515 of the Treasury and
General Government Appropriations
Act for Fiscal Year 2001 (Pub. L. 106–
554; H.R. 5658) and the associated
Information Quality Guidelines issued
by the Service, provide criteria,
establish procedures, and provide
guidance to ensure that decisions made
by the Service represent the best
scientific data available. They require
Service biologists, to the extent
consistent with the Act and with the use
of the best scientific data available, to
use primary and original sources of
information as the basis for
recommendations to designate critical
habitat. When determining which areas
are critical habitat, a primary source of
information is generally the listing
package for the species. Additional
information sources include the
recovery plan for the species, articles in
peer-reviewed journals, conservation
plans developed by States and counties,
scientific status surveys and studies,
biological assessments, or other
unpublished materials and expert
opinion or personal knowledge. All
information is used in accordance with
the provisions of Section 515 of the
Treasury and General Government
Appropriations Act for Fiscal Year 2001
(Pub. L. 106–554; H.R. 5658) and the
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associated Information Quality
Guidelines issued by the Service.
Section 4 of the Act requires that we
designate critical habitat on the basis of
the best scientific data available. Habitat
is often dynamic, and species may move
from one area to another over time.
Furthermore, we recognize that
designation of critical habitat may not
include all of the habitat areas that may
eventually be determined to be
necessary for the recovery of the
species. For these reasons, critical
habitat designations do not signal that
habitat outside the designation is
unimportant or may not be required for
recovery.
Areas that support populations but
are outside the critical habitat
designation will continue to be subject
to conservation actions implemented
under section 7(a)(1) of the Act and to
the regulatory protections afforded by
the section 7(a)(2) jeopardy standard, as
determined on the basis of the best
available information at the time of the
action. Federally funded or permitted
projects affecting listed species outside
their designated critical habitat areas
may still result in jeopardy findings in
some cases. Similarly, critical habitat
designations made on the basis of the
best available information at the time of
designation will not control the
direction and substance of future
recovery plans, habitat conservation
plans, or other species conservation
planning efforts if new information
available to these planning efforts calls
for a different outcome.
Methods
As required by section 4(b)(2) of the
Act, we used the best scientific data
available in determining areas that
contain the features that are essential to
the conservation of Acanthomintha
ilicifolia. This includes information
from the proposed listing rule (60 FR
40549, August 9, 1995); final listing rule
(63 FR 54938, October 13, 1998); data
from research and survey observations
published in peer-reviewed articles; site
visits and unpublished survey data;
regional Geographic Information System
(GIS) layers including soil, vegetation
and species coverages from San Diego
County and data compiled in the
California Natural Diversity Database
(CNDDB). More specifically, the
information sources used for this
proposal include: (1) CNDDB element
occurrence data (2005 and 2006); (2)
Bauder and McMillan (1994, pp. 1–87);
(3) McMillan (2001, pp. 1–91); (4)
herbarium records from San Diego
Natural History Museum, University of
California at Berkeley and Rancho Santa
Ana Botanical Garden; (5) personal
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communications with A. ilicifolia
experts (Bauder 2006; Hanson 2006;
Kelly 2005; McMillan 2006; Sproul
2006; and Vinje 2006); (6) site visits by
Service biologists to several known
element occurrences of A. ilicifolia in
2005 and 2006; and (7) information
provided by the Cleveland National
Forest of the U.S. Forest Service (Winter
and Young 2005).
Primary Constituent Elements
In accordance with section 3(5)(A)(i)
of the Act and regulations at 50 CFR
424.12, in determining which areas to
propose as critical habitat, we consider
those areas occupied by the species at
the time of listing that contain physical
or biological features (primary
constituent elements (PCEs)) that are
essential to the conservation of the
species, and that may require special
management considerations or
protection. These include, but are not
limited to, space for individual and
population growth and for normal
behavior; food, water, air, light,
minerals, or other nutritional or
physiological requirements; cover or
shelter; sites for breeding, reproduction,
and rearing of offspring, germination,
and seed dispersal; and habitats that are
protected from disturbance or are
representative of the historic
geographical and ecological
distributions of a species.
The specific primary constituent
element required for Acanthomintha
ilicifolia is derived from the biological
needs of A. ilicifolia as described in the
proposed and final listing rules (60 FR
40549; 63 FR 54938).
Space for Individual and Population
Growth and Normal Behavior
Acanthomintha ilicifolia occurs on
isolated patches of clay soils derived
from gabbro and soft calcareous
sandstone substrates (Oberbauer and
Vanderwier 1991, pp. 208–209) (PCE).
The soils derived from gabbro substrates
are red to dark brown clay soils, and
those derived from soft calcareous
sandstone are gray, sometimes loamy,
clay soils. These patches of clay soils
are called ‘‘clay lenses,’’ and in San
Diego County and northern Baja
California, Mexico, clay lenses are
known to support a variety of narrow
endemic (restricted to a specific
geographic area) plants. Clay lenses tend
to have an open or unpopulated look
because many common species cannot
tolerate living on these clay soils. Clay
lenses are typically devoid of woody,
perennial shrubs (PCE). It is believed
shrubs have difficulty surviving on
these soils because in the rainy winter
months these soils become saturated
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with water and the large root systems of
shrubs are not able to get oxygen
(Oberbauer and Vanderwier 1991, pp.
208–209). Also, as the soils become
saturated they expand and move, and
when the soils dry they contract and
crack, making it difficult for shrubs to
become established. Likewise, relatively
few common annual plant species
inhabit clay lenses due to the harsh
conditions, and those plants that are
adapted to these conditions, in some
cases, have become differentiated from
their common relatives. Due to the
absence of most common native
vegetation from these clay lenses, the
areas where A. ilicifolia occurs appear
as open areas in a matrix of coastal sage
scrub or chaparral (PCE).
Clay lenses are generally inhabited by
a specific flora that consist of forbs,
native grasses, and geophytes (perennial
plants propagated by buds on
underground bulbs, tubers, or corms
such as lilies, iris, and onions). Native
plant species that characterize the
vegetation found with Acanthomintha
ilicifolia on clay lenses include
Hesperevax sparsiflora var. sparsiflora
(erect evax), Harpagonella palmeri
(Palmer’s grappling-hook), Convolvulus
simulans (bindweed), Apiastrum
angustifolium (mock parsley), and
Microseris douglasii ssp. platycarpha
(small flowered microseris) (Bauder et
al. 1994, pp. 9–10; McMillan 2006, p. 1;
Vinje 2006b, pp. 1–2).
In addition to the characteristics
discussed above, the texture and
structure of the clay lenses are essential
for supporting the seedling
establishment and growth of
Acanthomintha ilicifolia. This soil
provides many small pockets where
seeds from A. ilicifolia become lodged
as they fall from decomposing plants
(Bauder and Sakrison 1999, p. 28). The
seeds then stay in the soils until the
temperatures become cooler in the
winter months and the soil becomes
saturated with the winter rains (Bauder
and Sakrison 1997, p. 28). The seedlings
then germinate and grow to mature
plants. These plants do best when they
are not crowded or shaded by other
plants (Bauder and Sakrison 1999, p.
12). The loose, crumbly texture of the
soil provides the proper substrate to
hold the seed bank and allow for root
growth (PCE).
Clay lenses generally form on gentle
slopes. An analysis of 20 sites where
Acanthomintha ilicifolia was observed
found that the slopes range from 0 to 25
degrees, with the majority of the sites
having slopes below 20 degrees (Bauder
et al. 1994, pp. 10–11) (PCE). This study
also found that many thriving, natural
populations were on slopes that faced
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southeast, south, southwest, and west,
although not all sites fit this pattern
(Bauder et al. 1994, pp. 10–11). Using
GIS, we found that the known
populations of Acanthomintha ilicifolia
range in elevation from sea level to
3,000 ft (914 m). Acanthomintha
ilicifolia occurs on several soil types.
These soils are mapped as Las Posas,
Olivenhain, Redding, Huerhuero,
Altamont, Cieneba, and Linne (Bowman
1973, pp. 22–24, 38–40, 54–55, 61–64,
67–68, and 71–72) and are derived from
gabbro and soft calcareous sandstone
substrates with a loose, crumbly
structure and deep fissures that provide
space for population and individual
growth and substrate for seedling
establishment.
Water and Hydrology
The loose, crumbly clay soils that
support Acanthomintha ilicifolia act
like a sponge and are saturated by
winter rains. The saturation of these
soils allows for seeds of A. ilicifolia to
imbibe with water and germinate in the
cool winter months (Bauder and
Sakrison 1997, p. 32). As such, the
species requires a natural hydrological
regime to reproduce. Since we do not
have specific information on the
hydrological regime that this species
requires, we did not include
hydrological regime as a primary
constituent element.
Reproduction and Pollination
The breeding system of
Acanthomintha ilicifolia has not been
studied, but it has been determined that
other members of the genus
Acanthomintha are self-compatible
(Steeck 1995, pp. 27–33). A 1996 study
(Bauder and Sakrison 1997, p. 38) found
that several insect species visited the
flowers and moved from plant to plant.
These insects represented possible
pollinators of A. ilicifolia; however,
none were thought to represent speciesspecific pollinators (Bauder and
Sakrison 1997, p. 39). Since we do not
have information on any speciesspecific pollinators that visit A.
ilicifolia, we did not include pollinators
as a primary constituent element.
Primary Constituent Elements for
Acanthomintha ilicifolia
Pursuant to our regulations, we are
required to identify the known physical
and biological features (PCEs) essential
to the conservation of Acanthomintha
ilicifolia.
Based on our current knowledge of
the life history, biology, and ecology of
the species and the requirements of the
habitat to sustain the essential life
history functions of the species, we have
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determined that the PCE for
Acanthomintha ilicifolia is:
Clay lenses that provide substrate for
seedling establishment and space for
growth and development of
Acanthomintha ilicifolia, that are:
(a) Within chaparral and coastal sage
scrub;
(b) On gentle slopes ranging from 0 to
25 degrees;
(c) Derived from gabbro and soft
calcareous sandstone substrates with a
loose, crumbly structure and deep
(approximately 2 feet (60 cm)) fissures;
and
(d) Characterized by a low density of
forbs and geophytes, and a low density
or absence of shrubs.
This proposed designation is designed
for the conservation of those areas
containing the PCE necessary to support
one or more of the species’ life history
functions. All units and subunits in this
proposed designation contain the PCE
and support multiple life processes.
This proposed rule would protect the
PCE and thus the conservation function
of the habitat.
Criteria Used To Identify Critical
Habitat
As required by section 4(b)(1)(A) of
the Act, we use the best scientific and
commercial data available in
determining areas that contain the
features that are essential to the
conservation of Acanthomintha
ilicifolia. All of the areas proposed for
designation are currently occupied by
the species. Occupied areas were
determined from survey data and
element occurrence data in the CNDDB
(CNDDB 2006). For the purpose of this
proposal, we assumed that each element
occurrence represents a population of A.
ilicifolia, except in cases where there are
several element occurrences located
within 1 mile (1.6 km) of each other and
the habitat is not fragmented by
manmade features. In these cases, we
considered the group of element
occurrences as a single population.
Examples of this include the
Manchester Preserve in Encinitas
(element occurrence (EO) 28, EO 42, and
EO 54), McGinty Mountain near Jamul
(EO 21, EO 22, and EO 30), and Viejas
and Poser Mountains near Alpine (EO
12, EO 50, EO 51, EO 62, EO 73, EO 74,
and EO 75).
We then identified the areas that
contain the features that are essential to
the conservation of A. ilicifolia by
identifying areas that: (1) Support
populations that occur on rare or unique
habitat within the species’ range; (2)
support the largest known populations
of A. ilicifolia; or (3) support stable
populations of A. ilicifolia. These
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criteria are explained in greater detail
below. Areas containing the primary
constituent elements and that meet at
least one of the above criteria were
considered for critical habitat
designation. To evaluate locations
occupied by this species we used: the
California Natural Diversity Database
(CNDDB 2006); a study by Bauder et al.
(1994); biological surveys (City of San
Diego 2000; City of San Diego 2001; City
of San Diego 2003; City of San Diego
2004; City of San Diego 2005;
Conservation Biology Institute 2002, p.
A3–1; County of San Diego 2002, p. 17;
Dudek and Associates, Inc. 2006,
Appendix A pp. 3–4; Helix
Environmental Planning, Inc. 2002, p. 6;
and REC Consultants, Inc. 2004, p.
figure 5); and interviews with botanists
working on this species (Kelley 2005;
McMillan 2006).
The first criterion we used to identify
proposed critical habitat was areas that
support populations that occur on rare
or unique habitat within the species’
range. The majority of areas that
currently support Acanthomintha
ilicifolia are on dark brown to reddish
brown clay soils that are derived from
gabbro substrates. Historically, A.
ilicifolia also occurred on gray clay soils
that are derived from soft calcareous
sandstone substrates. The only
remaining population on this soil type
is northeast of the intersection of
Palomar Airport Road and El Camino
Real, in the City of Carlsbad. Conserving
unique soil types that this species
occurs on will help to reduce the risk of
extinction for this species because it
may allow for the preservation of a
greater amount of genetic diversity
within the species’ gene pool. Therefore,
this area containing population (EO 70)
is proposed for critical habitat
designation under criterion one.
The second criterion we used to
identify proposed critical habitat was
areas that support the largest known
populations of Acanthomintha ilicifolia.
The CNDDB includes data for this
species that date back to 1978.
Populations of this species range from
just a few individual plants to several
thousand. The majority of the known
populations range from 50 to 2,000
plants. Yet, there are four populations
that stand out as the largest, each having
greater than 25,000 plants. The four
largest populations and the estimated
population at each location are:
Sycamore Canyon (EO 32), 31,000
plants; Slaughterhouse Canyon (EO 64),
60,000 plants; Viejas and Poser
Mountains (EO 12, EO 50, EO 51, EO 62,
EO 73, and EO 74), 29,650 plants; and
Hollenbeck Canyon (EO L), 100,000
plants. These large populations are vital
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for the conservation of this species
because they occur within large blocks
of open space and are less likely to be
impacted by edge effects associated with
smaller populations in highly urbanized
areas. Additionally, the conservation of
these large populations will increase the
persistence of the species across its
range. Therefore, the area containing
these populations is proposed for
critical habitat designation under
criterion two. These four populations
represent approximately 75 percent of
the total known plants of this species.
The third criterion we used to identify
proposed critical habitat was areas that
support stable populations of
Acanthomintha ilicifolia. For the
purpose of this proposed critical habitat
designation, we defined stable
populations as those that contained
more than 1,000 plants at least once
during the period for which we have
survey data. We evaluated the
population data from the CNDDB and
determined that populations with more
than 1,000 plants at one time had the
ability to rebound following years with
low population numbers. Therefore, we
considered populations with more than
1,000 plants to have a high probability
of persisting into the future and thus
contribute to the conservation of the
species. The locations of these
populations are generally characterized
by a series of clay lenses where the
plants are found in a matrix of intact
coastal sage scrub and chaparral.
Although these areas are not free from
exotic plant competitors, these
populations have persisted over time
without being out-competed by the
exotic plant species present. This may
be due in part to the low density of
exotic plant species at these locations.
In addition to all of the areas that meet
criterion two, five other areas meet
criterion three: the southeast portion of
the City of Carlsbad (EO 47); the
Manchester Preserve in Encinitas (EO
˜
28, EO 42, and EO 54); Los Penasquitos
Canyon (EO 19); Sabre Springs (EO 36);
and McGinty Mountain in the southern
part of San Diego County (EO 21, EO 22,
and EO 30). Each of these areas provides
habitat that consistently supports large
populations of A. ilicifolia. Therefore,
the area containing these populations is
proposed for critical habitat designation
under criterion three.
The 10 areas that we identified as
meeting the criteria for critical habitat
contain the features that are essential for
the conservation of this species. These
areas support the only population of
Acanthomintha ilicifolia on calcareous
clay soil and the largest and most stable
populations. These areas were mapped
using data from field surveys and
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11951
element occurrences in the CNDDB
(CNDDB 2006), and unit boundaries
were created using GIS.
Annual plants experience annual
fluctuation in population density and
spatial distribution. Through the review
of existing survey data and as a result
of field work conducted by Service
biologists, it appears that this holds true
for Acanthomintha ilicifolia, as
additional individuals are frequently
located outside initially mapped
occurrence areas (Bauder et al. 2004, pp.
14–15; CNDDB 2006, pp. 11, 28–29, and
70; Service unpublished data 2006).
Because soil data are not available on a
fine enough scale to ensure that
proposed critical habitat included all
occupied habitat, each area mapped for
A. ilicifolia in the CNDDB was enlarged
to include habitat within 500 ft (152 m)
around the edge of mapped occurrences.
Using aerial photography, we confirmed
that no identifiable portion of an
occupied clay lens appeared to have
been inadvertently omitted and
removed manmade features such as
roads, buildings, parking lots and
agricultural fields. This boundary was
then used as our proposed critical
habitat boundary.
When determining proposed critical
habitat boundaries within this proposed
rule, we made every effort to avoid
including developed areas such as lands
covered by buildings, paved areas, and
other structures that lack the PCE for
Acanthomintha ilicifolia. The scale of
the maps prepared under the parameters
for publication within the Code of
Federal Regulations may not reflect the
exclusion of such developed areas. Any
such structures and the land under them
inadvertently left inside critical habitat
boundaries shown on the maps of this
proposed rule have been excluded by
text in the proposed rule and are not
proposed for designation as critical
habitat. Therefore, Federal actions
limited to these areas would not trigger
section 7 consultation, unless they may
affect the species or primary constituent
elements in adjacent critical habitat.
We are proposing to designate critical
habitat on lands that we have
determined were occupied at the time of
listing that contain the PCE that
supports life history functions essential
for the conservation of the species and
lands that were not known to be
occupied at the time of listing, but that
we have determined are essential to the
conservation of the species. The lands
that were not known to be occupied at
the time of listing are all currently
occupied and contain the PCE essential
for the conservation of the species. The
10 areas defined above, each
representing one population, have been
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categorized into four units. Due to large
amounts of area that did not contain the
PCE in each of the four units, the units
were further broken down into 17
subunits so that the essential habitat
could be accurately mapped and not
include areas that do not have the PCE.
These units/subunits are described in
the Unit Descriptions section.
Section 10(a)(1)(B) of the Act
authorizes us to issue permits for the
take of listed animal species incidental
to otherwise lawful activities. An
incidental take permit application must
be supported by a habitat conservation
plan (HCP) that identifies conservation
measures that the permittee agrees to
implement for the species to minimize
and mitigate the impacts of the
requested incidental take. We often
exclude non-Federal public lands and
private lands that are covered by an
existing operative HCP and executed
implementation agreement (IA) under
section 10(a)(1)(B) of the Act from
designated critical habitat because the
benefits of exclusion outweigh the
benefits of inclusion as discussed in
section 4(b)(2) of the Act. While section
10(a)(1)(B) of the Act does not cover
take of listed plant species, HCPs often
cover both listed animal and plant
species. Acanthomintha ilicifolia is a
covered species in approved subarea
plans under two major HCPs, the San
Diego Multiple Species Conservation
Program (MSCP) and the San Diego
Habitat Conservation Program (MHCP).
We are proposing to exclude areas from
the final designation of critical habitat
where this species is covered by one of
these HCPs. See the Exclusions under
Section 4(b)(2) of the Act for a detailed
discussion of these exclusions. We
identify the areas proposed for
exclusion in the discussion of
individual critical habitat units below.
Special Management Considerations or
Protection
When designating critical habitat, we
assess whether the areas determined to
be occupied at the time of listing
contain primary constituent elements
that may require special management
considerations or protection.
As stated in the final listing rule,
threats to Acanthomintha ilicifolia
include trampling and grazing, the
presence of exotic plant species, offroad vehicles (ORVs), mining, and
urbanization (63 FR 54938). Through
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our review of the existing data on A.
ilicifolia, the threats listed in the final
listing rule continue to impact this
species and could impact the PCE as
well. Building on the information
contained in the final listing rule, data
on the effects of competition from exotic
plant species have been studied in
greater detail (Bauder and Sakrison
1999, pp. 6–19, 28–44) and attempts
have been made to manage this threat
(Kelly 2002, pp. 1–3).
Urban development near
Acanthomintha ilicifolia populations
may alter the habitat characteristics
required by the species. The destruction
of habitat can change the slope and
aspect of the site, making it
uninhabitable for A. ilicifolia (PCE). The
close proximity of development to
populations of A. ilicifolia may affect
other aspects of the site. For example,
increased water runoff from
developments may erode the clay lens
and change the topography of the site
(Bauder et al. 1994, p. 23) (PCE).
The introduction of exotic plant
species such as Centaurea melitensis
can drastically change the species
present in, and eliminate the open
character of, the clay lens habitat (PCE).
Centaurea melitensis has been shown,
in field and greenhouse experiments, to
negatively effect the biomass (growth)
and seed production (reproduction) of
Acanthomintha ilicifolia (Bauder and
Sakrison 1999, p. 16). Populations of A.
ilicifolia that are close to urbanized
areas or in areas that have been heavily
grazed generally have a high density of
exotic plant species. In disturbed soils,
C. melitensis is a common weed. When
this and other exotic plant species
become established they can outcompete A. ilicifolia for light, water,
nutrients, and space. A. ilicifolia often
grows larger and at a higher density
when competition with exotic weeds is
reduced (Bauder and Sakrison 1999, pp.
12–16; Vinje 2007, p. 10).
The final listing rule (63 FR 54938)
discusses the impacts of ORV activity
and trampling. In recent years the
impacts associated with the use of
mountain bikes has been observed to
cause similar impacts (Vinje 2006a, p.
1). Trampling, ORV activity, and
mountain bike use outside of
designated, maintained trails can
compact the loose, crumbly soils (PCE).
The repeated travel over a trail or track
degrades the habitat of Acanthomintha
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ilicifolia in two ways: (1) by displacing
soil; and (2) by compacting soil and
reducing the amount of water that can
percolate, thus reducing the plant’s
ability to establish roots.
Mining has been documented as a
threat at two sites known to support
Acanthomintha ilicifolia (63 FR 54938;
Bauder et al. 1994, p. 17). Mining can
alter many aspects of A. ilicifolia
habitat. Heavy machinery can compact
or remove clay lenses (PCE) or alter the
slope of an area (PCE). The grading of
large areas adjacent to A. ilicifolia
habitat can make those areas vulnerable
to invasion by exotic plant species and
lead to the subsequent crowding and
shading of A. ilicifolia habitat (PCE). All
of these impacts may in turn lead to the
disruption of the growth and
reproduction of A. ilicifolia .
Proposed Critical Habitat Designation
We are proposing a total of 1,936 ac
(783 ha) in four units as critical habitat
for Acanthomintha ilicifolia . These four
units are further subdivided into 17
subunits. The critical habitat areas
described below constitute our best
assessment at this time of areas known
to be occupied at the time of listing that
contain the primary constituent
elements that may require special
management considerations or
protection, and those additional areas
that were not known to be occupied at
the time of listing (subunits 3E and 4D),
but are essential to the conservation of
Acanthomintha ilicifolia . The four
units proposed for designation as
critical habitat are: (1) Unit 1: Northern
San Diego County; (2) Unit 2: Central
San Diego County; (3) Unit 3: Viejas
Mountain and Poser Mountain, San
Diego County; and (4) Unit 4: Southern
San Diego County. We are proposing to
exclude 1,302 ac (527 ha) under section
4(b)(2) of the Act from the final
designation of critical habitat. Table 1
identifies the occupancy status for each
subunit. Table 2 identifies the acreage
and ownership of the areas being
proposed as critical habitat and the
areas proposed for exclusion from the
final designation under section 4(b)(2)
of the Act (see Relationship of Critical
Habitat to Habitat Conservation Plan
Lands—Exclusions Under Section
4(b)(2) of the Act below for a detailed
discussion).
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TABLE 1.—OCCUPANCY OF PROPOSED CRITICAL HABITAT UNITS FOR ACANTHOMINTHA ILICIFOLIA
Known to be occupied to
the time of listing?
Occupied currently?
Yes .....................................
Yes .....................................
Yes .....................................
Yes .....................................
Yes .....................................
Yes .....................................
88 ac (36 ha)
73 ac (29 ha)
92 ac (37 ha)
Yes
Yes
Yes
Yes
.....................................
.....................................
.....................................
.....................................
Yes
Yes
Yes
Yes
.....................................
.....................................
.....................................
.....................................
63 ac (25 ha)
52 ac (22 ha)
306 ac (124 ha)
77 ac (31 ha)
Yes .....................................
Yes .....................................
Yes .....................................
Yes .....................................
No .......................................
Yes .....................................
Yes
Yes
Yes
Yes
Yes
Yes
.....................................
.....................................
.....................................
.....................................
.....................................
.....................................
33 ac (13 ha)
208 ac (84 ha)
318 ac (128 ha)
82 ac (33 ha)
34 ac (14 ha)
163 ac (66 ha)
Yes .....................................
Yes .....................................
Yes .....................................
No .......................................
Yes
Yes
Yes
Yes
.....................................
.....................................
.....................................
.....................................
18 ac (7 ha)
220 ac (89 ha)
27 ac (11 ha)
84 ac (34 ha)
.............................................
.............................................
Critical habitat unit
Unit 1: Northern San Diego County
1A. Palomar Airport (EO 70) ..................................................
1B. Southeast Carlsbad (EO 47) ............................................
1C. Manchester (EO 28, EO 42 and EO 54) .........................
Unit 2: Central San Diego County
˜
2A. Los Penasquitos Canyon (EO 19) ...................................
2B. Sabre Springs (EO 36) .....................................................
2C. Sycamore Canyon (EO 32) ..............................................
2D. Slaughterhouse Canyon (EO 64) .....................................
Unit 3: Viejas Mountain and Poser
Mountain 3A. Viejas Mountain (EO 73) ..................................
3B. Viejas Mountain (EO 50) ..................................................
3C. Viejas Mountain (EO 51) ..................................................
3D. Viejas Mountain (EO 62) ..................................................
3E. Poser Mountain (EO 74) ..................................................
3F. Poser Mountain (EO 12) ..................................................
Unit 4: Southern San Diego County
4A. McGinty Mountain (EO 21) ..............................................
4B. McGinty Mountain (EO 22) ..............................................
4C. McGinty Mountain (EO 30) ..............................................
4D. Hollenbeck Canyon (EO L) ..............................................
Total* ...................................................................................
Acres (hectares)
1,936 ac (783 ha)
* Some columns may not sum exactly due to rounding of values.
TABLE 2.—PROPOSED CRITICAL HABITAT FOR ACANTHOMINTHA ILICIFOLIA AND THE AREAS BEING PROPOSED FOR EXCLUSION FROM THE FINAL CRITICAL HABITAT DESIGNATION UNDER SECTION 4(B)(2) OF THE ACT (ACRES (AC), HECTARES
(HA), CNDDB ELEMENT OCCURRENCES (EO))
Unit 1: Northern San Diego County
1A. Palomar Airport (EO 70) ................
1B. Southeast Carlsbad (EO 47) ..........
1C. Manchester (EO 28, EO 42 and
EO 54).
Unit 2: Central San Diego County
˜
2A. Los Penasquitos Canyon (EO 19)
2B. Sabre Springs (EO 36) ...................
2C. Sycamore Canyon (EO 32) ............
2D. Slaughterhouse Canyon (EO 64) ...
Unit 3: Viejas Mountain and Poser Mountain
3A. Viejas Mountain (EO 73) ................
3B. Viejas Mountain (EO 50) ................
3C. Viejas Mountain (EO 51) ................
3D. Viejas Mountain (EO 62) ................
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3E. Poser Mountain (EO 74) ................
3F. Poser Mountain (EO 12) ................
Unit 4: Southern San Diego County
4A. McGinty Mountain (EO 21) ............
4B. McGinty Mountain (EO 22) ............
4C. McGinty Mountain (EO 30) ............
4D. Hollenbeck Canyon (EO L) ............
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Area being considered for exclusion
from final critical
habitat*
Land ownership
Critical habitat unit
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Area that meets the definition of critical habitat
Area proposed as critical
habitat
Private ................
State/Local ..........
Private ................
Private ................
7 ac (3 ha) ..........................
81 ac (33 ha) ......................
73 ac (29 ha) ......................
92 ac (37 ha) ......................
7 ac (3 ha) ..........................
81 ac (33 ha) ......................
73 ac (29 ha) ......................
92 ac (37 ha) ......................
7 ac (3 ha)
0 ac (0 ha)
73 ac (29 ha)
92 ac (37 ha)
State/Local ..........
Private ................
State/Local ..........
Private ................
State/Local ..........
Private ................
63 ac (25 ha) ......................
1 ac (1 ha) ..........................
51 ac (21 ha) ......................
30 ac (12 ha) ......................
276 ac (112 ha) ..................
77 ac (31 ha) ......................
63 ac (25 ha) ......................
1 ac (1 ha) ..........................
51 ac (21 ha) ......................
30 ac (12 ha) ......................
276 ac (112 ha) ..................
77 ac (31 ha) ......................
63 ac (25 ha)
1 ac (1 ha)
51 ac (21 ha)
30 ac (12 ha)
276 ac (112 ha)
77 ac (31 ha)
Private
Private
Federal
Private
Federal
Private
Federal
Federal
Private
Federal
................
................
...............
................
...............
................
...............
...............
................
...............
33 ac (13 ha) ......................
156 ac (63 ha) ....................
52 ac (21 ha) ......................
38 ac (15 ha) ......................
280 ac (113 ha) ..................
50 ac (20 ha) ......................
32 ac (13 ha) ......................
34 ac (14 ha) ......................
7 ac (3 ha) ..........................
156 ac (63 ha) ....................
33 ac (13 ha) ......................
156 ac (63 ha) ....................
52 ac (21 ha) ......................
38 ac (15 ha) ......................
280 ac (113 ha) ..................
50 ac (20 ha) ......................
32 ac (13 ha) ......................
34 ac (14 ha) ......................
7 ac (3 ha) ..........................
156 ac (63 ha) ....................
33 ac (13 ha)
156 ac (63 ha)
0 ac (0 ha)
38 ac (15 ha)
0 ac (0 ha)
50 ac (20 ha)
0 ac (0 ha)
0 ac (0 ha)
7 ac (3 ha)
0 ac (0 ha)
Private ................
Private ................
State/Local ..........
Private ................
Private ................
State/Local ..........
18 ac (7 ha) ........................
210 ac (85 ha) ....................
10 ac (4 ha) ........................
27 ac (11 ha) ......................
23 ac (9 ha) ........................
61 ac (25 ha) ......................
18 ac (7 ha) ........................
210 ac (85 ha) ....................
10 ac (4 ha) ........................
27 ac (11 ha) ......................
23 ac (9 ha) ........................
61 ac (25 ha) ......................
18 ac (7 ha)
210 ac (85 ha)
10 ac (4 ha)
27 ac (11 ha)
23 ac (9 ha)
61 ac (25 ha)
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TABLE 2.—PROPOSED CRITICAL HABITAT FOR ACANTHOMINTHA ILICIFOLIA AND THE AREAS BEING PROPOSED FOR EXCLUSION FROM THE FINAL CRITICAL HABITAT DESIGNATION UNDER SECTION 4(B)(2) OF THE ACT (ACRES (AC), HECTARES
(HA), CNDDB ELEMENT OCCURRENCES (EO))—Continued
Land ownership
Critical habitat unit
Total ** ...............................................
Area that meets the definition of critical habitat
Area proposed as critical
habitat
.............................
1,936 ac (783 ha) ...............
1,936 ac (783 ha) ...............
Area being considered for exclusion
from final critical
habitat*
1,302 ac (527 ha)
* Lands proposed for exclusion from final critical habitat under section 4(b)(2) of the Act due to the conservation provided for Acanthomintha
ilicifolia from the City of Carlsbad and City of Encinitas subarea plans of the San Diego MHCP and the City of San Diego and County of San
Diego subarea plans of the San Diego MSCP.
** Some columns may not sum exactly due to rounding of values.
Below, we present brief descriptions
of all units and subunits, and reasons
why they meet the definition of critical
habitat for Acanthomintha ilicifolia. The
PCE in each subunit of critical habitat
is threatened by the presence of exotic
plants and recreational activities (e.g.,
trampling, erosion and soil compaction
caused by hiking, off-road vehicle
activity, and mountain biking);
therefore, special management
considerations or protections of the PCE
is required to address these threats.
cprice-sewell on PROD1PC66 with PROPOSALS2
Unit Descriptions
Unit 1: Northern San Diego County
Unit 1 consists of 253 ac (102 ha) in
northern San Diego County divided into
three subunits. This critical habitat unit
includes habitat for Acanthomintha
ilicifolia in the cities of Carlsbad and
Encinitas under private, State, and local
ownership (Table 1). The majority of
habitat for A. ilicifolia in northern San
Diego County is located in proximity to
residential and commercial
development; however, the habitat
being proposed as critical habitat is
mostly on land that has been set aside
for the conservation of this and other
species. This unit contains five element
occurrences, all of which were known at
the time of listing. The majority of the
element occurrences in this unit are
covered by the San Diego Multiple
Habitat Conservation Program (MHCP).
As part of the MHCP, each city will
complete a subarea plan. At this time,
the City of Carlsbad has completed its
subarea plan under the San Diego
MHCP and the City of Encinitas is
nearing the completion of its subarea
plan. We are proposing to exclude 172
ac (70 ha) in the City of Carlsbad
(portions of Subunit 1A and all of
Subunit 1B) and the City of Encinitas
(Subunit 1C) from the final designation
of critical habitat based on protections
afforded to A. ilicifolia under the
Carlsbad and Encinitas subarea plans of
the MHCP (see Relationship of Critical
Habitat to Habitat Conservation Plan
Lands—Exclusions Under Section
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4(b)(2) of the Act below for more
information). The remaining 81 ac (33
ha) in Subunit 1A is owned by the
County of San Diego and is not part the
San Diego MHCP.
Subunit 1A, Palomar Airport (EO 70)
Subunit 1A consists of 88 ac (36 ha)
and was known to be occupied at the
time of listing. This subunit contains
several habitat patches known to
support Acanthomintha ilicifolia and
contains the feature (PCE) considered to
be essential to the conservation of the
species. The subunit meets our selection
criteria because it supports a population
on a unique soil type (criterion 1). This
is the only area where A. ilicifolia is still
known to occupy calcareous clay soils.
The PCE in this subunit may require
special management considerations or
protection to control exotic plant
species and reduce impacts associated
with recreational activities. This subunit
is within the designated preserve area
for the Carlsbad subarea plan (referred
to as the Carlsbad Habitat Management
Plan (HMP)) of the San Diego MHCP;
however, most of this subunit is owned
by the County of San Diego and not a
part of the Carlsbad HMP. The portion
covered by the Carlsbad HMP will be
managed for the conservation of this
species. Therefore, we are proposing to
exclude the 7 ac (3 ha) of this subunit
that are covered by the Carlsbad HMP
from the final designation of critical
habitat (Table 1) (see Relationship of
Critical Habitat to Habitat Conservation
Plan Lands—Exclusions Under Section
4(b)(2) of the Act below for more
information). The remaining 81 ac (33
ha) of land owned by the County of San
Diego is proposed for inclusion in the
designation of critical habitat.
Subunit 1B, Southeast Carlsbad (EO 47)
Subunit 1B consists of 73 ac (29 ha),
was known to be occupied at the time
of listing, and contains the feature (PCE)
considered to be essential to the
conservation of the species. The subunit
meets our selection criteria because it
supports a stable population (criterion
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3). This population was estimated to
have 400 plants in 1989, 2,000 plants in
1994, and 500 plants in 2006. The PCE
in this subunit may require special
management considerations or
protection to control exotic plant
species and reduce impacts associated
with recreational activities. The
majority of the lands within this subunit
are within an area designated as a
hardline conservation area (an area that
has already been or is slated to be
preserved) and the entire subunit is
covered by the Carlsbad HMP of the San
Diego MHCP which will provide
substantial protection and management
of the PCE essential to the conservation
of Acanthomintha ilicifolia. Therefore,
we are proposing to exclude this
subunit from the final designation of
critical habitat (Table 1) (see
Relationship of Critical Habitat to
Habitat Conservation Plan Lands—
Exclusions Under Section 4(b)(2) of the
Act below for more information).
Subunit 1C, Manchester (EO 42, EO 28,
and EO 54)
Subunit 1C consists of 92 ac (37 ha),
was known to be occupied at the time
of listing, and contains the feature (PCE)
considered to be essential to the
conservation of the species. The subunit
meets our selection criteria because it
supports a stable population (criterion
3). This population was estimated to
have 5,000 plants in 1984, 300 plants in
1985, 100 plants in 1986, 571 plants in
1989, 2,000 plants in 1990, 4,000 plants
in 1999, 5,000 plants in 1994, 3,000
plants in 2005, and 500 plants in 2006.
The PCE in this subunit may require
special management considerations or
protection to control exotic plant
species and reduce impacts associated
with recreational activities.
Lands within this subunit are within
a Focused Planning Area (core areas and
linkages important for conservation of
sensitive species) as designated under
the City of Encinitas subarea plan of the
San Diego MHCP. This plan indicates
that the City of Encinitas will complete
the HCP process under the San Diego
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MHCP and implement the conservation
measures outlined for Acanthomintha
ilicifolia. We are proposing to exclude
all non-Federal lands in Subunit 1C
covered by the City of Encinitas subarea
plan of the San Diego MHCP from the
final designation of critical habitat
pursuant to section 4(b)(2) of the Act
(Table 1) (see Relationship of Critical
Habitat to Habitat Conservation Plan
Lands—Exclusions Under Section
4(b)(2) of the Act below for more
information). However, since it is our
understanding that little progress has
been made by the City of Encinitas to
finalize their subarea plan since the
2001 release of the draft plan, we are
seeking public comment on our
proposed exclusion (see Public
Comments Solicited section above).
Based on information received during
the public comment period, the
Secretary may determine that sufficient
progress has not been made and that
lands within the City of Encinitas’
subarea plan should not be excluded
from the final designation of critical
habitat.
cprice-sewell on PROD1PC66 with PROPOSALS2
Unit 2: Central San Diego County
Unit 2 consists of 497 ac (201 ha)
divided into four subunits. This unit is
located in central San Diego County.
This critical habitat unit includes
habitat for Acanthomintha ilicifolia in
the City of San Diego and in portions of
unincorporated County of San Diego
under private, State, and local
ownership (Table 1). The majority of
habitat for A. ilicifolia in Unit 2 is
located within preserves and open
space; however, the PCE in this unit
may require special management
considerations or protection to control
exotic plant species and reduce impacts
associated with recreational activities.
All of the element occurrences included
in Unit 2 are protected under the
approved City of San Diego and County
of San Diego subarea plans under the
San Diego Multiple Species
Conservation Program (MSCP);
therefore, we are proposing to exclude
all four subunits from the final
designation of critical habitat (see
Relationship of Critical Habitat to
Habitat Conservation Plan Lands—
Exclusions Under Section 4(b)(2) of the
Act below for more information).
˜
Subunit 2A, Penasquitos Canyon (EO
19)
Subunit 2A consists of 63 ac (25 ha),
was known to be occupied at the time
of listing, and contains the feature (PCE)
considered to be essential to the
conservation of the species. The subunit
meets our selection criteria because it
supports a stable population (criterion
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3). This population was estimated to
have 1,000 plants in 1986, 740 plants in
1990, 14 plants in 1991, 36 plants in
1992, 1,800 plants in 1994, 1,053 plants
in 2000, 601 plants in 2001, 0 plants in
2002, 726 plants in 2003, 501 plants in
2004, and 2,091 plants in 2005. The PCE
in this subunit may require special
management considerations or
protection to control exotic plant
species and reduce impacts associated
with recreational activities. This area is
covered under the City of San Diego
subarea plan of the San Diego MSCP
and is within an area designated as a
hardline conservation area. Therefore,
we are proposing to exclude this area
from the final designation of critical
habitat (Table 1) (see Relationship of
Critical Habitat to Habitat Conservation
Plan Lands—Exclusions Under Section
4(b)(2) of the Act below for more
information).
Subunit 2B, Sabre Springs (EO 36)
Subunit 2B consists of 52 ac (22 ha),
was known to be occupied at the time
of listing, and contains the feature (PCE)
considered to be essential to the
conservation of the species. The subunit
meets our selection criteria because it
supports a stable population (criterion
3). This population was estimated to
have 5,970 plants in 1989, 2,900 plants
in 1990, 7,000 plants in 1992, 16,400
plants in 1994, 3,858 plants in 2000,
2,832 plants in 2001, 250 plants in 2002,
19,721 plants in 2003, 17,085 plants in
2004, 13 plants in 2005, and 150 plants
in 2006. The PCE in this subunit may
require special management
considerations or protection to control
exotic plant species and reduce impacts
associated with recreational activities.
This area is covered under the City of
San Diego subarea plan of the San Diego
MSCP and is within an area designated
as a hardline conservation area.
Therefore, we are proposing to exclude
this area from the final designation of
critical habitat (Table 1) (see
Relationship of Critical Habitat to
Habitat Conservation Plan Lands—
Exclusions Under Section 4(b)(2) of the
Act below for more information).
Subunit 2C, Sycamore Canyon (EO 32)
Subunit 2C consists of 306 ac (144
ha), was known to be occupied at the
time of listing, and contains the feature
(PCE) considered to be essential to the
conservation of the species. The subunit
meets our selection criteria because it is
one of the largest recorded populations
of Acanthomintha ilicifolia and it
supports a stable population (criteria 2
and 3). This population was estimated
to have 3,000 plants in 1986, 200 plants
in 1989, 8,800 plants in 1992, and
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11955
31,000 plants in 1994. The PCE in this
subunit may require special
management considerations or
protection to control exotic plant
species and reduce impacts associated
with recreational activities. In the San
Diego MSCP analysis, this area was
recognized as one of eight ‘‘major
populations.’’ This area is covered
under the County of San Diego subarea
plan of the San Diego MSCP and is
within an area designated as a hardline
conservation area; therefore, we are
proposing to exclude this area from the
final designation of critical habitat
(Table 1) (see Relationship of Critical
Habitat to Habitat Conservation Plan
Lands—Exclusions Under Section
4(b)(2) of the Act below for more
information).
Subunit 2D, Slaughterhouse Canyon (EO
64)
Subunit 2D consists of 77 ac (31 ha),
was known to be occupied at the time
of listing, and contains the feature (PCE)
considered to be essential to the
conservation of the species. The subunit
meets our selection criteria because it
supports one of the largest recorded
populations of Acanthomintha ilicifolia
(criterion 2). This population was
estimated to have 60,000 plants in 1993.
The PCE in this subunit may require
special management considerations or
protection to control exotic plant
species and reduce impacts associated
with recreational activities. In the San
Diego MSCP analysis, this area was
recognized as one of eight major
populations. The element occurrence of
A. ilicifolia at this site is on open space
adjacent to a sand and gravel mining
operation. This element occurrence is
covered under the County of San Diego
subarea plan of the San Diego MSCP.
Therefore, we are proposing to exclude
this area from the final designation of
critical habitat (Table 1) (see
Relationship of Critical Habitat to
Habitat Conservation Plan Lands—
Exclusions Under Section 4(b)(2) of the
Act below for more information).
Unit 3: Viejas Mountain and Poser
Mountain
Unit 3 consists of 837 ac (339 ha)
divided into six subunits in interior San
Diego County. This critical habitat unit
includes habitat for Acanthomintha
ilicifolia in the City of Alpine and in the
Cleveland National Forest on Viejas and
Poser Mountains. The majority of
habitat for A. ilicifolia in this unit is
located on land managed by the U.S.
Forest Service (USFS) (Table 1). The
element occurrences that are on Viejas
and Poser Mountains are interspersed in
clay patches in a mosaic of relatively
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undisturbed habitat. Due to the
proximity of these element occurrences
and the fact that the habitat is not
fragmented by any manmade barriers,
these element occurrences are
considered to be a single population of
A. ilicifolia. This unit is proposed for
critical habitat designation because it
supports one of the largest recorded
populations of the species (criterion 2).
This population is estimated to have
greater than 30,000 plants based on the
maximum number of plants observed at
the different element occurrences (EO
12, 6,650 plants in 1991; EO 50, 5,600
plants in 1994; EO 51, 8,300 plants in
2003; EO 62, 1,115 plants in 2000; EO
73, 8,750 plants in 1997; and EO 74,
2,000 plants in 2000). The PCE in this
unit may require special management to
control exotic plant species. This unit
has some areas that are protected as part
of the San Diego MSCP. We are
proposing to exclude non-Federal lands
covered by the County of San Diego
subarea plan of the San Diego MSCP in
this unit (284 ac (115 ha)) from the final
designation of critical habitat (Table 1)
(see Relationship of Critical Habitat to
Habitat Conservation Plan Lands—
Exclusions Under Section 4(b)(2) of the
Act below for more information).
cprice-sewell on PROD1PC66 with PROPOSALS2
Subunit 3A, Viejas Mountain (EO 73)
Subunit 3A consists of 33 ac (13 ha),
was known to be occupied at the time
of listing, and contains the feature (PCE)
considered to be essential to the
conservation of the species. Subunit 3A
is privately owned and covered by the
County of San Diego subarea plan of the
San Diego MSCP (33 ac (13 ha)). The
PCE in this subunit may require special
management considerations or
protection to control exotic plant
species and reduce impacts associated
with recreational activities. Because the
County of San Diego subarea plan
provides for the conservation of
Acanthomintha ilicifolia and this
subunit is within a hardline
conservation area, we are proposing to
exclude all of this subunit from the final
designation of critical habitat (Table 1)
(see Relationship of Critical Habitat to
Habitat Conservation Plan Lands—
Exclusions Under Section 4(b)(2) of the
Act below for more information).
Subunit 3B, Viejas Mountain (EO 50)
Subunit 3B consists of 208 ac (84 ha),
was known to be occupied at the time
of listing, and contains the feature (PCE)
considered to be essential to the
conservation of the species. Subunit 3B
includes land managed by the USFS and
land under private ownership. The
privately owned land is covered by the
County of San Diego subarea plan of the
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San Diego MSCP (156 ac (63 ha)). The
PCE in this subunit may require special
management considerations or
protection to control exotic plant
species and reduce impacts associated
with recreational activities. Because the
County of San Diego subarea plan
provides for the conservation of
Acanthomintha ilicifolia, we are
proposing to exclude the portion of this
subunit on private land from the final
designation of critical habitat (Table 1)
(see Relationship of Critical Habitat to
Habitat Conservation Plan Lands—
Exclusions Under Section 4(b)(2) of the
Act below for more information). The
remaining 52 ac (21 ha) of federally
owned land is proposed for inclusion in
the designation of critical habitat.
Subunit 3C, Viejas Mountain (EO 51)
Subunit 3C consists of 318 ac (129
ha), was known to be occupied at the
time of listing, and contains the feature
(PCE) considered to be essential to the
conservation of the species. Subunit 3C
includes land managed by the USFS and
land under private ownership. The
privately owned land is covered by the
County of San Diego subarea plan of the
San Diego MSCP (38 ac (15 ha)), some
of which falls within a hardline
conservation area. The PCE in this
subunit may require special
management considerations or
protection to control exotic plant
species and reduce impacts associated
with recreational activities. Because the
County of San Diego subarea plan
provides for the conservation of
Acanthomintha ilicifolia, we are
proposing to exclude the portion of this
subunit on private land from the final
designation of critical habitat (Table 1)
(see Relationship of Critical Habitat to
Habitat Conservation Plan Lands—
Exclusions Under Section 4(b)(2) of the
Act below for more information). The
remaining 280 ac (113 ha) of federally
owned land is proposed for inclusion in
the designation of critical habitat.
Subunit 3D, Viejas Mountain (EO 62)
Subunit 3D consists of 82 ac (33 ha),
was known to be occupied at the time
of listing, and contains the feature (PCE)
considered to be essential to the
conservation of the species. Subunit 3D
includes land managed by the USFS and
land under private ownership. The
privately owned land is covered by the
County of San Diego subarea plan of the
San Diego MSCP (50 ac (20 ha)), some
of which falls within a hardline
conservation area. The PCE in this
subunit may require special
management considerations or
protection to control exotic plant
species and reduce impacts associated
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with recreational activities. Because the
County of San Diego subarea plan
provides for the conservation of
Acanthomintha ilicifolia, we are
proposing to exclude the portion of this
subunit on private land from the final
designation of critical habitat (Table 1)
(see Relationship of Critical Habitat to
Habitat Conservation Plan Lands—
Exclusions Under Section 4(b)(2) of the
Act below for more information). The
remaining 32 ac (13 ha) of federally
owned land is proposed for inclusion in
the designation of critical habitat.
Subunit 3E, Poser Mountain (EO 74)
Subunit 3E consists of 34 ac (14 ha)
and was not known to be occupied at
the time of listing; however, this area is
currently occupied and contains the
PCE. This area containing population
(EO 74) is essential to the conservation
of Acanthomintha ilicifolia because it
meets criterion 2 for designation of
critical habitat in that it is a portion of
the four largest known populations of A.
ilicifolia. Based on our analysis of
reported density estimates, this subunit
contains approximately 6 percent of
individuals in the greater Poser and
Viejas Mountain population. In 2000,
when this population was discovered, it
totaled 2,000 plants. This subunit is on
land managed by the USFS. No
exclusions are proposed for this
subunit. Therefore, 34 ac (14 ha) of
federally owned land is proposed for
inclusion in the final designation of
critical habitat.
Subunit 3F, Poser Mountain (EO 12)
Subunit 3F consists of 163 ac (66 ha),
was known to be occupied at the time
of listing, and contains the feature (PCE)
considered to be essential to the
conservation of the species. Subunit 3F
includes land managed by the USFS and
land under private ownership. The
privately owned land is covered by the
County of San Diego subarea plan of the
San Diego MSCP (7 ac (3 ha)), some of
which falls within a hardline
conservation area. The PCE in this unit
may require special management
considerations or protection to control
exotic plant species and reduce impacts
associated with recreational activities.
Because the County of San Diego
subarea plan provides for the
conservation of Acanthomintha
ilicifolia, we are proposing to exclude
the portion of this subunit on private
land from the final designation of
critical habitat (Table 1) (see
Relationship of Critical Habitat to
Habitat Conservation Plan Lands—
Exclusions Under Section 4(b)(2) of the
Act below for more information). The
remaining 156 ac (63 ha) of federally
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owned land is proposed for inclusion in
the designation of critical habitat.
Unit 4: Southern San Diego County
Unit 4 consists of 351 ac (142 ha)
divided into four subunits in southern
San Diego County. This critical habitat
unit includes habitat for Acanthomintha
ilicifolia near the City of Jamul in the
southern portion of the unincorporated
County of San Diego that is under
private, State, and local ownership
(Table 1). The habitat for A. ilicifolia in
southern San Diego County is located in
proximity to rural residential
development and in relatively
undeveloped areas. This unit has many
element occurrences that are protected
as part of the San Diego MSCP and
included in the subarea plan for the
County of San Diego. All of the land
proposed for critical habitat in this unit
is covered by this subarea plan.
Therefore, we propose to exclude all
four subunits covered by the San Diego
MSCP from the final designation of
critical habitat (see Relationship of
Critical Habitat to Habitat Conservation
Plan Lands—Exclusions Under Section
4(b)(2) of the Act below for more
information).
cprice-sewell on PROD1PC66 with PROPOSALS2
Subunits 4A, 4B, and 4C, McGinty
Mountain (EO 21, EO 22, and EO 30)
Effects of Critical Habitat Designation
Subunits 4A, 4B, and 4C consist of
265 ac (107 ha), were known to be
occupied at the time of listing, and
contain the feature (PCE) considered to
be essential to the conservation of the
species. These sites include three
element occurrences occupied by
Acanthomintha ilicifolia on McGinty
Mountain, and due to the proximity of
these element occurrences, they are
considered to be a single population.
This population was estimated to have
1,200 plants in 1986, and 2,625 plants
in 1994. The PCE in this unit may
require special management
considerations or protection to control
exotic plant species and reduce impacts
associated with recreational activities.
In the San Diego MSCP analysis, this
area was considered one of eight major
populations discussed in the plan. This
population is included in the County of
San Diego subarea plan of the San Diego
MSCP and is within an area designated
as a hardline conservation area.
Therefore, we are proposing to exclude
the entirety of these subunits from the
final designation of critical habitat
(Table 1) (see Relationship of Critical
Habitat to Habitat Conservation Plan
Lands—Exclusions Under Section
4(b)(2) of the Act below for more
information).
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Subunit 4D, Hollenbeck Canyon (EO L)
Subunit 4D consists of 84 ac (34 ha)
and was not known to be occupied at
the time of listing; however it is
currently occupied and contains the
PCE. This site is on the Hollenbeck
Canyon Wildlife Area, a preserve owned
and managed by the California
Department of Fish and Game. This area
is essential to the conservation of the
species because it meets criterion 2 for
designation of critical habitat in that it
contains approximately 100,000 plants,
the largest known population of
Acanthomintha ilicifolia; almost twice
as large as the next largest population at
Slaughterhouse Canyon (EO 64), that
has 60,000 plants. The population in
this subunit was estimated to contain
30,000 plants in 2002 which suggests
active recruitment at this location. This
population is included in the County of
San Diego subarea plan of the San Diego
MSCP and the majority of the subunit is
within an area designated as a hardline
conservation area. Therefore, we are
proposing to exclude all of this subunit
from the final designation of critical
habitat (Table 1) (see Relationship of
Critical Habitat to Habitat Conservation
Plan Lands—Exclusions Under Section
4(b)(2) of the Act below for more
information).
Section 7 Consultation
Section 7 of the Act requires Federal
agencies, including the Service, to
ensure that actions they fund, authorize,
or carry out are not likely to destroy or
adversely modify critical habitat. In our
regulations at 50 CFR 402.02, we define
destruction or adverse modification as
‘‘a direct or indirect alteration that
appreciably diminishes the value of
critical habitat for both the survival and
recovery of a listed species. Such
alterations include, but are not limited
to, alterations adversely modifying any
of those physical or biological features
that were the basis for determining the
habitat to be critical.’’ However, recent
decisions by the 5th and 9th Circuit
Court of Appeals have invalidated this
definition (see Gifford Pinchot Task
Force v. U.S. Fish and Wildlife Service,
378 F. 3d 1059 (9th Cir 2004) and Sierra
Club v. U.S. Fish and Wildlife Service,
245 F.3d 434, 442F (5th Cir 2001)).
Pursuant to current national policy and
the statutory provisions of the Act,
destruction or adverse modification is
determined on the basis of whether,
with implementation of the proposed
Federal action, the affected critical
habitat would remain functional (or
retain the current ability for the primary
constituent elements to be functionally
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established) to serve the intended
conservation role for the species.
Section 7(a) of the Act requires
Federal agencies, including the Service,
to evaluate their actions with respect to
any species that is proposed or listed as
endangered or threatened and with
respect to its critical habitat, if any is
proposed or designated. Regulations
implementing this interagency
cooperation provision of the Act are
codified at 50 CFR part 402.
Section 7(a)(4) of the Act requires
Federal agencies to confer with us on
any action that is likely to jeopardize
the continued existence of a species
proposed for listing or result in
destruction or adverse modification of
proposed critical habitat. This is a
procedural requirement only. However,
once a proposed species becomes listed,
or proposed critical habitat is
designated as final, the full prohibitions
of section 7(a)(2) of the Act apply to any
Federal action. The primary utility of
the conference procedures is to
maximize the opportunity for a Federal
agency to adequately consider proposed
species and critical habitat and avoid
potential delays in implementing their
proposed action as a result of the
section 7(a)(2) compliance process,
should those species be listed or the
critical habitat designated.
Under conference procedures, the
Service may provide advisory
conservation recommendations to assist
the agency in eliminating conflicts that
may be caused by the proposed action.
The Service may conduct either
informal or formal conferences. Informal
conferences are typically used if the
proposed action is not likely to have any
adverse effects to the proposed species
or proposed critical habitat. Formal
conferences are typically used when the
Federal agency or the Service believes
the proposed action is likely to cause
adverse effects to proposed species or
critical habitat, inclusive of those that
may cause jeopardy or adverse
modification.
The results of an informal conference
are typically transmitted in a conference
report, while the results of a formal
conference are typically transmitted in a
conference opinion. Conference
opinions on proposed critical habitat are
typically prepared according to 50 CFR
402.14, as if the proposed critical
habitat were designated. We may adopt
the conference opinion as the biological
opinion when the critical habitat is
designated, if no substantial new
information or changes in the action
alter the content of the opinion (see 50
CFR 402.10(d)). As noted above, any
conservation recommendations in a
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conference report or opinion are strictly
advisory.
If a species is listed or critical habitat
is designated, section 7(a)(2) of the Act
requires Federal agencies to ensure that
activities they authorize, fund, or carry
out are not likely to jeopardize the
continued existence of such a species or
to destroy or adversely modify its
critical habitat. If a Federal action may
affect a listed species or its critical
habitat, the responsible Federal agency
(action agency) must enter into
consultation with us. As a result of this
consultation, compliance with the
requirements of section 7(a)(2) of the
Act will be documented through the
Service’s issuance of: (1) A concurrence
letter for Federal actions that may affect,
but are not likely to adversely affect,
listed species or critical habitat; or (2) a
biological opinion for Federal actions
that are likely to adversely affect listed
species or critical habitat.
When we issue a biological opinion
concluding that a project is likely to
result in jeopardy to a listed species or
the destruction or adverse modification
of critical habitat, we also provide
reasonable and prudent alternatives to
the project, if any are identifiable.
‘‘Reasonable and prudent alternatives’’
are defined at 50 CFR 402.02 as
alternative actions identified during
consultation that can be implemented in
a manner consistent with the intended
purpose of the action, that are consistent
with the scope of the Federal agency’s
legal authority and jurisdiction, that are
economically and technologically
feasible, and that the Director believes
would avoid jeopardy to the listed
species or destruction or adverse
modification of critical habitat.
Reasonable and prudent alternatives can
vary from slight project modifications to
extensive redesign or relocation of the
project. Costs associated with
implementing a reasonable and prudent
alternative are similarly variable.
Regulations at 50 CFR 402.16 require
Federal agencies to reinitiate
consultation on previously reviewed
actions in certain instances, including
where a new species is listed or critical
habitat is subsequently designated that
may be affected by the Federal action,
where the Federal agency has retained
discretionary involvement or control
over the action or such discretionary
involvement or control is authorized by
law. Consequently, some Federal
agencies may request reinitiation of
consultation with us on actions for
which formal consultation has been
completed, if those actions may affect
subsequently listed species or
designated critical habitat or adversely
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modify or destroy proposed critical
habitat.
Federal activities that may affect
Acanthomintha ilicifolia or its
designated critical habitat will require
section 7 consultation under the Act.
Activities on State, Tribal, local, or
private lands requiring a Federal permit
(such as a permit from the Army Corps
of Engineers under section 404 of the
Clean Water Act or a permit under
section 10(a)(1)(B) of the Act from the
Service) or involving some other Federal
action (such as funding from the Federal
Highway Administration, Federal
Aviation Administration, or the Federal
Emergency Management Agency) will
also be subject to the section 7
consultation process. Federal actions
not affecting listed species or critical
habitat, and actions on State, Tribal,
local, or private lands that are not
federally funded, authorized, or
permitted, do not require section 7
consultations.
Application of the Jeopardy and
Adverse Modification Standards for
Actions Involving Effects to
Acanthomintha ilicifolia and Its Critical
Habitat
Jeopardy Standard
The Service applies an analytical
framework for Acanthomintha ilicifolia
jeopardy analyses that relies heavily on
the importance of core area populations
to the survival and recovery of A.
ilicifolia. The section 7(a)(2) analysis is
focused not only on these populations
but also on the habitat conditions
necessary to support them.
The jeopardy analysis usually
expresses the survival and recovery
needs of Acanthomintha ilicifolia in a
qualitative fashion without making
distinctions between what is necessary
for survival and what is necessary for
recovery. Generally, if a proposed
Federal action is incompatible with the
viability of the affected core area
population(s), inclusive of associated
habitat conditions, a jeopardy finding is
considered to be warranted because of
the relationship of each core area
population to the survival and recovery
of the species as a whole.
Adverse Modification Standard
If this proposal is adopted, the
analytical framework described in the
Director’s December 9, 2004,
memorandum will be used to complete
section 7(a)(2) analyses for Federal
actions affecting Acanthomintha
ilicifolia critical habitat. The key factor
related to the adverse modification
determination is whether, with
implementation of the proposed Federal
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action, the affected critical habitat
would remain functional (or retain the
current ability for the primary
constituent elements to be functionally
established) to serve the intended
conservation role for the species.
Generally, the conservation role of A.
ilicifolia critical habitat units is to
support viable core area populations.
Section 4(b)(8) of the Act requires us
to briefly evaluate and describe in any
proposed or final regulation that
designates critical habitat those
activities involving a Federal action that
may destroy or adversely modify such
habitat, or that may be affected by such
designation. Activities that may destroy
or adversely modify critical habitat may
also jeopardize the continued existence
of the species.
Activities that may destroy or
adversely modify critical habitat are
those that alter the PCE to an extent that
the conservation value of critical habitat
for Acanthomintha ilicifolia is
appreciably reduced. Activities that,
when carried out, funded, or authorized
by a Federal agency, may affect critical
habitat and therefore result in
consultation for A. ilicifolia include, but
are not limited to:
(1) Actions that would disturb or
remove the clay soils within a subunit
of critical habitat. Such activities could
include, but are not limited to, clearing
areas for development and roads,
creation of trails, and installation of
pipelines or other underground
infrastructure. These activities could
eliminate or reduce the habitat
necessary for the growth and
reproduction of Acanthomintha
ilicifolia.
(2) Actions that would introduce
exotic plant species or alter the natural
habitat in a way that increases the
likelihood for the invasion of exotic
plant species. Such activities could
include, but are not limited to, the
introduction of fill dirt to development
sites adjacent to Acanthomintha
ilicifolia critical habitat, grading areas
for agriculture, clearing native
vegetation, and the use of mountain
bikes and off-highway vehicles. These
activities could create space for
populations of exotic plants to grow and
then invade A. ilicifolia habitat or bring
the seeds of exotic plants into A.
ilicifolia habitat, thus filling the open
space needed for the growth and
reproduction of this species with exotic
plant competitors.
(3) Actions that would alter the
hydrology of critical habitat subunits.
Such activities could include, but are
not limited to, runoff from developed
streets, runoff from irrigated landscapes,
and increased flow or erosion from
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storm drains. These activities could
alter the timing and amount of water
that Acanthomintha ilicifolia plants
receive, altering their phenology and
fecundity. These activities could also
cause the erosion of the clay soils that
are necessary for the growth of A.
ilicifolia.
We consider all of the units proposed
as critical habitat, as well as those that
have been proposed for exclusion from
the final designation, to contain features
essential to the conservation of
Acanthomintha ilicifolia. All units are
within the geographic range of the
species, all units except 3E and 4D were
occupied by the species at the time of
listing, and all units are currently
occupied (based on observations made
within the last 15 years). Federal
agencies already consult with us on
activities in areas currently occupied by
A. ilicifolia, or if the species may be
affected by the action, to ensure that
their actions do not jeopardize the
continued existence of A. ilicifolia.
Exclusions Under Section 4(b)(2) of the
Act
There are multiple ways to provide
management or protection for species’
habitat. Statutory and regulatory
frameworks that exist at a local level can
provide protection or management, as
can lack of pressure for change, such as
areas too remote for anthropogenic
disturbance. Finally, State, local, or
private management plans, as well as
management under Federal agencies’
jurisdictions, can provide protection or
management that may lessen or even
eliminate any appreciable benefit to a
designation of critical habitat. When we
consider a plan to determine its
adequacy in protecting habitat, we
consider whether the plan, as a whole,
will provide the same level of protection
that designation of critical habitat
would provide. The plan need not lead
to exactly the same result as a
designation in every individual
application, as long as the protection it
provides is equivalent, overall. In
making this determination, we examine
whether the plan provides management,
protection, or enhancement of the PCEs
that is at least equivalent to that
provided by a critical habitat
designation, and whether there is a
reasonable expectation that the
management, protection, or
enhancement actions will continue into
the foreseeable future. Each review is
particular to the species and the plan,
and some plans may be adequate for
some species and inadequate for others.
Section 4(b)(2) of the Act states that
critical habitat shall be designated, and
revised, on the basis of the best
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available scientific data after taking into
consideration the economic impact,
national security impact, and any other
relevant impact of specifying any
particular area as critical habitat. The
Secretary may exclude an area from
critical habitat if he determines that the
benefits of such exclusion outweigh the
benefits of specifying such area as part
of the critical habitat, unless he
determines, based on the best scientific
data available, that the failure to
designate such area as critical habitat
will result in the extinction of the
species. In making that determination,
the Secretary is afforded broad
discretion, and the Congressional record
is clear that in making a determination
under the section the Secretary has
discretion as to which factors to use and
how much weight will be given to any
factor.
Under section 4(b)(2) of the Act, in
considering whether to exclude a
particular area from the designation, we
must identify the benefits of including
the area in the designation, identify the
benefits of excluding the area from the
designation, and determine whether the
benefits of exclusion outweigh the
benefits of inclusion. If an exclusion is
contemplated, then we must determine
whether excluding the area would result
in the extinction of the species. In the
following sections, we address a number
of general issues that are relevant to the
exclusions we considered. In addition,
the Service is conducting an economic
analysis of the impacts of the proposed
critical habitat designation and related
factors, which will be available for
public review and comment. Based on
public comment on that document, the
proposed designation itself, and the
information in the final economic
analysis, areas in addition to those
proposed for exclusion here may be
excluded from critical habitat by the
Secretary under the provisions of
section 4(b)(2) of the Act. This is
provided for in the Act, and in our
implementing regulations at 50 CFR
424.19.
Conservation Partnerships on NonFederal Lands
Most federally listed species in the
United States will not recover without
the cooperation of non-Federal
landowners. More than 60 percent of the
United States is privately owned
(National Wilderness Institute 1995),
and at least 80 percent of endangered or
threatened species occur either partially
or solely on private lands (Crouse et al.
2002). Stein et al. (1995) found that only
about 12 percent of listed species were
found almost exclusively on Federal
lands (90–100 percent of their known
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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
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.
Many non-Federal landowners derive
satisfaction in contributing to
endangered species recovery. The
Service promotes these private-sector
efforts through the Four Cs
philosophy—conservation through
communication, consultation, and
cooperation. This philosophy is evident
in Service programs such as HCPs, Safe
Harbor Agreements, Candidate
Conservation Agreements, Candidate
Conservation Agreements with
Assurances, and conservation challenge
cost-share. Many private landowners,
however, are wary of the possible
consequences of encouraging
endangered species to their property,
and there is mounting evidence that
some regulatory actions by the Federal
government, while well-intentioned and
required by law, can under certain
circumstances have unintended
negative consequences for the
conservation of species on private lands
(Wilcove et al. 1996; Bean 2002; Conner
and Mathews 2002; James 2002; Koch
2002, Brook et al. 2003). Many
landowners fear a decline in their
property value due to real or perceived
restrictions on land-use options where
threatened or endangered species are
found. Consequently, harboring
endangered species is viewed by many
landowners as a liability, resulting in
anti-conservation incentives because
maintaining habitats that harbor
endangered species represents a risk to
future economic opportunities (Main et
al. 1999; Brook et al. 2003).
The purpose of designating critical
habitat is to contribute to the
conservation of threatened and
endangered species and the ecosystems
upon which they depend. The outcome
of the designation, triggering regulatory
requirements for actions funded,
authorized, or carried out by Federal
agencies under section 7 of the Act, can
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sometimes be counterproductive to its
intended purpose on non-Federal lands.
According to some researchers, the
designation of critical habitat on private
lands significantly reduces the
likelihood that landowners will support
and carry out conservation actions
(Main et al. 1999; Bean 2002; Brook et
al. 2003). The magnitude of this
negative outcome is greatly amplified in
situations where active management
measures (e.g., reintroduction, fire
management, control of invasive
species) are necessary for species
conservation (Bean 2002). The Service
believes that the judicious exclusion of
specific areas of non-federally owned
lands from critical habitat designation
can contribute to species recovery and
provide a superior level of conservation
than critical habitat alone.
The Department of Interior’s
Cooperative Conservation philosophy is
the foundation for developing the tools
of conservation. These tools include
conservation grants, funding for
Partners for Fish and Wildlife Program,
the Coastal Program, and cooperativeconservation challenge cost-share
grants. Our Private Stewardship Grant
program and Landowner Incentive
Program provide assistance to private
landowners in their voluntary efforts to
protect threatened, imperiled, and
endangered species, including the
development and implementation of
HCPs.
Conservation agreements with nonFederal landowners (e.g., HCPs,
contractual conservation agreements,
easements, and stakeholder-negotiated
State regulations) enhance species
conservation by extending protections
for species beyond those available
through section 7 consultations. In the
past decade, we have encouraged nonFederal landowners to enter into
conservation agreements, based on a
view that we can achieve greater species
conservation on non-Federal land
through such partnerships than we can
through coercive methods (61 FR 63854;
December 2, 1996).
General Principles of Section 7
Consultations Used in the 4(b)(2)
Balancing Process
The most direct, and potentially
largest, regulatory benefit of critical
habitat is that federally authorized,
funded, or carried out activities require
consultation pursuant to 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
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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.
Once consultation under section 7 of
the Act is triggered, the process may
conclude informally when the Service
concurs in writing that the proposed
Federal action is not likely to adversely
affect the listed species or its critical
habitat. However, if the Service
determines through informal
consultation that adverse impacts are
likely to occur, then formal consultation
would be initiated. Formal consultation
concludes with a biological opinion
issued by the Service on whether the
proposed Federal action is likely to
jeopardize the continued existence of a
listed species or result in destruction or
adverse modification of critical habitat,
with separate analyses being made
under both the jeopardy and the adverse
modification standards. For critical
habitat, a biological opinion that
concludes in a determination of no
destruction or adverse modification may
contain discretionary conservation
recommendations to minimize adverse
effects to primary constituent elements,
but it would not contain any mandatory
reasonable and prudent measures or
terms and conditions. Mandatory
measures and terms and conditions to
implement such measures are only
specified when the proposed action
would result in the incidental take of a
listed animal or species. Reasonable and
prudent alternatives to the proposed
Federal action would only be suggested
when the biological opinion results in a
jeopardy or adverse modification
conclusion.
We also note that for 30 years prior to
the Ninth Circuit Court’s decision in
Gifford Pinchot Task Force v. U.S. Fish
and Wildlife Service, 378 F.3d 1059 (9th
Cir 2004) (hereinafter Gifford Pinchot),
the Service conflated the jeopardy
standard with the standard for
destruction or adverse modification of
critical habitat when evaluating Federal
actions that affect currently occupied
critical habitat. The Court ruled that the
two standards are distinct and that
adverse modification evaluations
require consideration of impacts on the
recovery of species. Thus, under the
Gifford Pinchot decision, critical habitat
designations may provide greater
benefits to the recovery of a species.
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However, we believe the conservation
achieved through implementing HCPs
or other habitat management plans is
typically greater than would be
achieved through multiple site-by-site,
project-by-project, section 7
consultations involving consideration of
critical habitat. Management plans
commit resources to implement longterm management and protection to
particular habitat for at least one and
possibly other listed or sensitive
species. Section 7 consultations only
commit Federal agencies to prevent
adverse modification to critical habitat
caused by the particular project, and
they are not committed to provide
conservation or long-term benefits to
areas not affected by the proposed
project. Thus, any HCP or management
plan which considers enhancement or
recovery as the management standard
will often provide as much or more
benefit than a consultation for critical
habitat designation conducted under the
standards required by the Ninth Circuit
in the Gifford Pinchot decision.
The information provided in this
section applies to all the discussions
below that discuss the benefits of
inclusion and exclusion of critical
habitat in that it provides the framework
for the consultation process.
Educational Benefits of Critical Habitat
A 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 Acanthomintha ilicifolia. In
general, the educational benefit of a
critical habitat designation always
exists, although in some cases it may be
redundant with other educational
effects. For example, HCPs have
significant public input and may largely
duplicate the educational benefit of a
critical habitat designation. This benefit
is closely related to a second, more
indirect benefit: that designation of
critical habitat would inform State
agencies and local governments about
areas that could be conserved under
State laws or local ordinances.
However, we believe that there would
be little additional informational benefit
gained from the designation of critical
habitat for the exclusions we are
proposing in this rule because these
areas are identified as having habitat
containing the features essential to the
conservation of the species.
Consequently, we believe that the
informational benefits are already
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provided even though these areas are
not designated as critical habitat.
Additionally, the purpose normally
served by the designation, that of
informing State agencies and local
governments about areas that would
benefit from protection and
enhancement of habitat for
Acanthomintha ilicifolia is already well
established among State and local
governments, and Federal agencies, in
those areas that we are proposing to
exclude from critical habitat in this rule
on the basis of other existing habitat
management protections.
The information provided in this
section applies to all the discussions
below that discuss the benefits of
inclusion and exclusion of critical
habitat.
Benefits of Excluding Lands With HCPs
or Other Approved Management Plans
From Critical Habitat
The benefits of excluding lands with
HCPs or other approved management
plans from critical habitat designation
include relieving landowners,
communities, counties, and States of
any additional regulatory burden that
may occur through a critical habitat
designation. Most HCPs and other
conservation plans take many years to
develop and, upon completion, are
consistent with the recovery objectives
for listed species that are covered within
the plan area. Many conservation plans
not only provide conservation benefits
to federally listed species, but also to
unlisted sensitive species. Imposing an
additional layer of regulatory review as
a result of the designation of critical
habitat may undermine these
conservation efforts and partnerships in
many areas where HCPs or management
plans exist or are being developed.
Designation of critical habitat within the
boundaries of management plans that
provide conservation measures for a
species could be viewed as a
disincentive to those entities currently
developing these plans or contemplating
them in the future, because one of the
incentives for undertaking conservation
is greater ease of permitting where listed
species are affected. The addition of a
new regulatory requirement would
remove a significant incentive for
undertaking the time and expense of
management planning. In fact,
designating critical habitat in areas
covered by a pending HCP or
conservation plan could result in the
loss of some conservation benefits to the
species if participants abandon the
planning process, in part because of the
strength of the perceived additional
regulatory compliance that such
designation would entail. The time and
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cost of regulatory compliance for a
critical habitat designation do not have
to be quantified for them to be perceived
as additional Federal regulatory burden
sufficient to discourage continued
participation in plans targeting listed
species’ conservation.
A related benefit of excluding lands
within an HCP or other management
plan from critical habitat designation is
the unhindered, continued ability to
seek new partnerships with future plan
participants including States, counties,
local jurisdictions, conservation
organizations, and private landowners,
which together can implement
conservation actions that we would be
unable to accomplish otherwise. If lands
within approved HCP or other
management plan areas are designated
as critical habitat, it would likely have
a negative effect on our ability to
establish new partnerships to develop
these plans, particularly plans that
address landscape-level conservation of
species and their habitats. By excluding
these lands, we preserve our current
partnerships and encourage additional
conservation actions in the future.
Furthermore, an HCP or Natural
Communities Conservation Plan
(NCCP)/HCP application must itself be
consulted upon, even without the
critical habitat designation. Such a
consultation would review the effects of
all activities covered by the HCP that
might adversely impact the species
under a jeopardy standard, including
possibly significant habitat modification
(see definition of ‘‘harm’’ at 50 CFR
17.3). In addition, Federal actions not
covered by the HCP in areas occupied
by listed species would still require
consultation under section 7 of the Act
and would be reviewed for possibly
significant habitat modification in
accordance with the definition of harm
referenced above.
The information provided in this
section applies to all the discussions
below that discuss the benefits of
inclusion and exclusion of critical
habitat.
Exclusions Under Section 4(b)(2) of the
Act for Acanthomintha ilicifolia
After consideration under section
4(b)(2) of the Act, we are proposing to
exclude the following areas from critical
habitat for Acanthomintha ilicifolia:
private lands covered by the San Diego
Multiple Habitat Conservation Program
in subunits 1A, 1B, and 1C and private
lands covered by the San Diego Multiple
Species Conservation Program in
subunits 2A, 2B , 2C, 2D, 3A, 3B, 3C,
3D, 3F, 4A, 4B, 4C, and 4D. We believe
that: (1) The value of these lands for
conservation has been addressed by
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existing protective actions, or (2) it is
appropriate to exclude these lands
pursuant to the ‘‘other relevant factor’’
provisions of section 4(b)(2) of the Act.
We specifically solicit comment,
however, on the inclusion or exclusion
of such areas. A detailed analysis of our
exclusion of these lands under section
4(b)(2) of the Act is provided in the
paragraphs that follow.
Relationship of Critical Habitat to
Habitat Conservation Plan Lands—
Exclusions Under Section 4(b)(2) of the
Act
We consider a current plan to provide
adequate management or protection if it
meets three criteria: (1) The plan is
complete and provides the same or
better level of protection from adverse
modification or destruction than that
provided through a consultation under
section 7 of the Act; (2) there is a
reasonable expectation that the
conservation management strategies and
actions will be implemented based on
past practices, written guidance, or
regulations; and (3) the plan provides
conservation strategies and measures
consistent with currently accepted
principles of conservation biology. We
believe that the following HCPs fulfill
these criteria for Acanthomintha
ilicifolia: the City of San Diego subarea
plan, the County of San Diego subarea
plan, the City of Poway subarea plan,
the City of Chula Vista subarea plan
under the San Diego MSCP, and the City
of Carlsbad subarea plan under the San
Diego MHCP. We are considering the
exclusion of non-Federal lands covered
by these plans that provide for the
conservation of A. ilicifolia from the
final designation of critical habitat
pursuant to section 4(b)(2) of the Act.
We also consider HCP covered lands
for exclusion under 4(b)(2) of the Act if
the plans are approaching completion
and, when completed, will meet the
above criteria. We have proposed
critical habitat in one subarea plan that
has not yet been completed. The City of
Encinitas completed a final draft
subarea plan that was released for
public review in 2001. This plan
indicates that the City of Encinitas will
complete the HCP process under the
San Diego MHCP and implement the
conservation measures outlined for
Acanthomintha ilicifolia. However, it is
our understanding that little progress
has been made by the City of Encinitas
to finalize their subarea plan since the
2001 release of the draft plan. Therefore,
we are seeking public comment on our
proposal to exclude 92 ac (37 ha) of
non-Federal lands in Subunit 1C
covered by the City of Encinitas subarea
plan of the San Diego MHCP pursuant
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to section 4(b)(2) of the Act (see Public
Comments Solicited section above).
Based on information received during
the public comment period, the
Secretary may determine that sufficient
progress has not been made and that
lands within the City of Encinitas’
subarea plan should not be excluded
from the final designation of critical
habitat.
To aid in the public review of this
proposed critical habitat, we are
providing maps of the areas that we are
proposing to exclude. Maps and GIS
layers for areas proposed for exclusion
are available from the Carlsbad Fish and
Wildlife Office (see ADDRESSES) and on
our website at https://carlsbad.fws.gov/
sdtm.htm.
San Diego Multiple Habitat
Conservation Program (MHCP)
We are proposing to exclude from the
final critical habitat designation
approximately 172 ac (70 ha) of nonFederal lands within the City of
Carlsbad subarea plan and the City of
Encinitas subarea plans of the San Diego
MHCP under section 4(b)(2) of the Act.
The San Diego MHCP includes the
following subareas: City of Carlsbad,
City of Encinitas, City of Escondido,
City of Oceanside, City of San Marcos,
and City of Vista. We are proposing to
exclude 7 ac (3 ha) in Subunit 1A and
73 ac (29 ha) in Subunit 1B covered
under the City of Carlsbad subarea plan,
and 92 ac (37 ha) in Subunit 1C which
will be covered under the City of
Encinitas subarea plan. This exclusion
pertains to all but 7ac (3 ha) of land
proposed as critical habitat in Unit 1.
Only the City of Carlsbad subarea plan
is completed and legally operative;
however the City of Encinitas completed
a final draft subarea plan that was
released for public review in 2001. Once
in place, the City of San Marcos, City of
Oceanside, City of Escondido, and City
of Vista subarea plans will also provide
for the conservation of A. ilicifolia;
however, no critical habitat has been
proposed within these cities. The City of
Carlsbad and City of Encinitas subarea
plans provide for special management
and protection for the physical and
biological features essential for the
conservation of A. ilicifolia that exceed
the level of regulatory control that
would be afforded this species by the
designation of critical habitat. We
believe that the benefits of excluding
proposed critical habitat covered by
these HCPs from the critical habitat
designation would outweigh the
benefits of including them as critical
habitat and that the exclusion under
consideration would not result in the
extinction of A. ilicifolia.
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The San Diego MHCP is a
comprehensive, multi-jurisdictional,
planning program designed to create,
manage, and monitor an ecosystem
preserve in northwestern San Diego
County. The San Diego MHCP is also a
regional subarea plan under the State of
California’s Natural Communities
Conservation Plan (NCCP) program and
was developed in cooperation with
California Department of Fish and Game
(CDFG). The MHCP preserve system is
intended to protect viable populations
of native plant and animal species and
their habitats in perpetuity, while
accommodating continued economic
development and quality of life for
residents of northern San Diego County.
The MHCP includes an approximately
112,000-ac (45,324-ha) study area
within the cities of Carlsbad, Encinitas,
Escondido, San Marcos, Oceanside,
Vista and Solana Beach.
The 10(a)(1)(B) permit for the City of
Carlsbad HMP was issued on November
9, 2004. Acanthomintha ilicifolia is a
conditionally covered species under the
HMP. ‘‘Conditional’’ coverage means
that the City of Carlsbad receives take
authorization under the Act for this
species as long as they comply with the
conservation measures outlined in the
HMP. Under the MHCP, the majority of
the known populations fall within
Focused Planning Areas (FPA) (core
areas and linkages important for
conservation of sensitive species) and
will be conserved at levels of 95 to 100
percent. Populations that fall outside of
FPAs will be conserved at a minimum
80 percent level based on the Narrow
Endemic Plant policy. The Narrow
Endemic Policy requires the
conservation of new populations of
narrow endemic species (80 percent
outside of FPAs) and mitigation for
unavoidable impacts as well as
management practices designed to
achieve no net loss of narrow endemic
populations. In addition, cities cannot
permit more than 5 percent gross
cumulative loss of narrow endemic
populations or occupied acreage within
the Focused Planning Areas and no
more than 20 percent cumulative loss of
narrow endemic locations, population
numbers, or occupied acreage outside of
Focused Planning Areas (AMEC Earth
and Environmental, Inc. 2003).
According to the MHCP, 91 percent of
the major populations and critical
locations of this species (as identified in
the MHCP) in the study area will be
conserved under the FPA design. In
addition to conserved point localities,
an estimated 3,403 acres of potentially
suitable habitat will be conserved as a
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result of the existing preserve design
and preserve policies.
The subarea plan for the City of
Encinitas follows the same framework
under the MHCP, allowing for similar
conservation and management of known
A. ilicifolia populations. Areas that
contain features essential to the
conservation of the species that fall
within the boundaries of both the City
of Carlsbad and the City of Encinitas
subarea plans under the MHCP will be
incorporated into the preserve areas,
and provisions to manage the
populations within the preserve areas
will provide for the long-term
conservation of the species.
Benefits of Exclusion Outweigh the
Benefits of Inclusion
We expect the approved City of
Carlsbad subarea plan and the City of
Encinitas subarea plan, once approved,
to provide substantial protection and
management of the PCE essential to the
conservation of Acanthomintha
ilicifolia on lands in Subunit 1A (7 ac
(3 ha)), Subunit 1B (73 ac (29 ha)), and
Subunit 1C (92 ac (37 ha)). We expect
the subarea plans to provide active
management for A. ilicifolia on nonFederal lands in contrast to designation
of critical habitat, which would only
preclude their destruction or adverse
modification. Moreover, the educational
benefits that would result from critical
habitat designation, including informing
the public of areas that are necessary for
the long-term conservation of the
species, are already in place both as a
result of material provided on our
website and through public notice-andcomment procedures required to
establish the MHCP and associated
subarea plans.
In contrast to the lack of an
appreciable benefit of including these
lands as critical habitat, the exclusion of
these lands from critical habitat will
help preserve the partnerships that we
have developed with the local
jurisdictions and project proponents in
the development of the MHCP and
associated subarea plans. As discussed
above, many landowners perceive
critical habitat as an unfair and
unnecessary regulatory burden given the
expense and time involved in
developing and implementing complex
regional HCPs, such as the MHCP. For
these reasons, we believe that
designating critical habitat has little
benefit in areas covered by subarea
plans of the MHCP, and such minor
benefit is outweighed by the benefits of
maintaining partnerships with local
jurisdictions and private landowners
with lands covered by the MHCP.
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We have reviewed and evaluated the
benefits of inclusion and the benefits of
exclusion of lands as critical habitat for
Acanthomintha ilicifolia. Based on this
evaluation, we find that the benefits of
excluding lands in areas covered by the
City of Carlsbad and City of Encinitas
subarea plans of the MHCP outweigh
the benefits of including those lands as
critical habitat for A. ilicifolia.
cprice-sewell on PROD1PC66 with PROPOSALS2
Exclusion Will Not Result in Extinction
of the Species
Exclusion of these 172 ac (70 ha) of
non-Federal lands from the final
designation of critical habitat would not
result in the extinction of
Acanthomintha ilicifolia because these
lands will be permanently conserved
and managed for the benefit of this
species pursuant to the MHCP subarea
plans. The jeopardy standard of section
7 and routine implementation of habitat
protection through the section 7 process
also provide assurances that the species
will not go extinct. The protections
afforded to A. ilicifolia under the
jeopardy standard will remain in place
for the areas proposed for exclusion
from critical habitat.
San Diego Multiple Species
Conservation Program (MSCP)
We are proposing to exclude from the
final critical habitat designation
approximately 1,130 ac (457 ha) of nonFederal lands within the City of San
Diego subarea plan and the County of
San Diego subarea plan of the San Diego
MSCP under section 4(b)(2) of the Act.
We propose to exclude 63 ac (25 ha) in
Subunit 2A and 52 ac (22 ha) in Subunit
2B covered by the City of San Diego
subarea plan, and 306 ac (124 ha) in
Subunit 2C, 77 ac (31 ha) in Subunit 2D,
33 ac (13 ha) in Subunit 3A, 156 ac (63
ha) in Subunit 3B, 38 ac (15 ha) in
Subunit 3C, 50 ac (20 ha) in Subunit 3D,
7 ac (3 ha) in Subunit 3F, 18 ac (7 ac)
in Subunit 4A, 220 ac (89 ha) in Subunit
4B, 27 ac (11 ha) in Subunit 4C, and 84
ac (34 ha) in Subunit 4D covered by the
County of San Diego subarea plan of the
San Diego MSCP. Acanthomintha
ilicifolia is a covered species under
these two approved and legally
operative subarea plans. The City of
Poway and the City of Chula Vista have
subarea plans that also provide for the
conservation of A. ilicifolia; however,
no critical habitat has been proposed
within the City of Poway or the City of
Chula Vista. These HCPs provide
special management and protection for
the physical and biological features
essential for the conservation of A.
ilicifolia that exceed the level of
regulatory control that would be
afforded this species by the designation
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of critical habitat. We believe that the
benefits of excluding proposed critical
habitat covered by these HCPs from the
critical habitat designation would
outweigh the benefits of including them
as critical habitat and that the exclusion
under consideration would not result in
the extinction of A. ilicifolia.
In southwestern San Diego County,
the MSCP effort encompasses more than
582,000 ac (236,000 ha) and anticipates
the participation of 12 jurisdictions.
Under the broad umbrella of the MSCP,
each of the 12 participating jurisdictions
prepares a subarea plan that implements
the goals of the MSCP within that
particular jurisdiction. Four of the 12
jurisdictions cover lands that support
Acanthomintha ilicifolia. All four of
these jurisdictions, the City of San
Diego, the City of Chula Vista, the
County of San Diego, and the City of
Poway, have approved subarea plans.
We conduct a consultation on each
subarea plan and associated permit
under section 7 of the Act to ensure they
are not likely to result in jeopardy or
adversely modify or destroy the
designated critical habitat of any
covered species. We also review the
plans under Section 10 of the Act to
ensure they meet the criteria for
issuance of an incidental take permit
and are consistent with the terms and
goals of the MSCP. We completed these
analyses for the City of San Diego, the
City of Chula Vista, the County of San
Diego, and the City of Poway subarea
plans prior to issuing incidental take
permits to the jurisdictions.
The regional MSCP is also a regional
subarea plan under the State of
California’s Natural Communities
Conservation Plan (NCCP) program and
was developed in cooperation with
California Department of Fish and Game
(CDFG). Over the 50-year term of the
City and County permits, the MSCP
provides for the establishment of
approximately 171,000 ac (69,573 ha) of
preserve lands within the Multi-Habitat
Planning Area (MHPA) (City of San
Diego) and Pre-Approved Mitigation
Areas (PAMA) (County of San Diego) to
benefit the 85 federally listed and
sensitive species, including
Acanthomintha ilicifolia, covered under
the plan. Private lands within the
MHPA and PAMA lands are subject to
special restrictions on development and,
as they are committed to the preserve,
must be legally protected and
permanently managed to conserve the
covered species. Public lands owned by
the City and County and by the State of
California and Federal government that
are identified for conservation under the
MSCP must also be protected and
permanently managed to protect the
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11963
covered species. The MSCP requires the
City and County to develop broad
framework and site-specific
management plans, subject to the review
and approval of the Service and CDFG,
to guide the management of all preserve
lands under City and County control.
The plans incorporate requirements to
monitor and adaptively manage A.
ilicifolia habitats over time. Under the
MSCP, the State and Federal
governments have also committed to
provide similar management for their
preserve lands.
As discussed above, each take
authorization holder must prepare a
framework management plan. The
framework management plan provides
general direction for all preserve
management issues within the subarea
plan’s boundaries. Area-specific
management directives are developed
for managing lands that are conserved as
part of the reserves. The framework and
area-specific management plans are
comprehensive and address a broad
range of management needs at the
preserve and species levels. These plans
include the following: (1) Fire
management; (2) public access control;
(3) fencing and gates; (4) ranger patrol;
(5) trail maintenance; (6) visitor/
interpretive and volunteer services; (7)
hydrological management; (8) signage
and lighting; (9) trash and litter removal;
(10) access road maintenance; (11)
enforcement of property and/or
homeowner requirements; (12) removal
of invasive species; (13) nonnative
predator control; (14) species
monitoring; (15) habitat restoration; (16)
management for diverse age classes; (17)
use of herbicides and rodenticides; (18)
biological surveys; (19) research; and
(20) species management conditions
(Final MSCP Plan 1998). These
management measures benefit
Acanthomintha ilicifolia and reduce the
threats to this species. The MSCP also
provides for a biological monitoring
program for A. ilicifolia (Final MSCP
Plan 1998). The City of San Diego
monitors A. ilicifolia on an annual basis
(City of San Diego 2000; 2001; 2003;
2004; and 2005). Moreover, the rare
plant monitoring under the MSCP is
being evaluated and updated with the
assistance of the U.S. Geological Survey
Biological Research Division and a
three-member, independent, scientific
advisory group.
In addition to the restrictions on
development and conservation
obligations that apply within the
Multiple Habitat Planning Area (MHPA)
and Pre-Approved Mitigation Area
(PAMA), the MSCP incorporates
processes to protect sensitive species of
limited distribution, including
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Acanthomintha ilicifolia, within the
plan area. Under the City of San Diego’s
subarea plan, impacts to narrow
endemic species inside the MHPA will
be avoided and outside the MHPA will
be protected as appropriate by (1)
avoidance, (2) management, (3)
enhancement, and/or (4) transplantation
to areas identified for preservation.
Under the County of San Diego’s
subarea plan, narrow endemic plants,
including A. ilicifolia, would be
conserved under their Biological
Mitigation Ordinance using a process
that (1) requires avoidance to the
maximum extent feasible, (2) allows for
a maximum 20 percent encroachment
into a population if total avoidance is
not feasible, and (3) requires mitigation
at the 1:1 to 3:1 (in kind) for impacts if
avoidance and minimization of impacts
would result in no reasonable use of the
property. Thus, these processes to
protect narrow endemic plants,
including A. ilicifolia, whether located
on lands targeted for preserve status
within the MHPA and PAMA or located
outside of those areas, ensure these
limited distribution species are
protected wherever they occur.
Considered as a whole, the protection
and management of A. ilicifolia
provided under the City and County
subarea plans will ensure the permanent
conservation of this species and its
habitat within the areas covered by the
plans.
We therefore propose to exclude from
the final critical habitat designation all
of Unit 2 and Unit 4 and the nonFederal portion of Unit 3 under section
4(b)(2) of the Act because these lands
are covered by the City of San Diego and
the County of San Diego subarea plans.
Populations of Acanthomintha ilicifolia
that occur within these subarea plan
areas will be conserved and will be
managed and monitored pursuant to the
MSCP. The framework and area-specific
management plans will provide
management and monitoring of A.
ilicifolia.
Benefits of Exclusion Outweigh the
Benefits of Inclusion
We expect the City of San Diego and
the County of San Diego subarea plans
to provide substantial protection and
management of habitat that contains
features essential to the conservation of
Acanthomintha ilicifolia in areas
covered by these plans. We expect these
subarea plans to provide active
management for A. ilicifolia on nonFederal lands in contrast to designation
of critical habitat, which would only
preclude their destruction or adverse
modification. Moreover, the educational
benefits that would result from critical
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habitat designation, including informing
the public of areas that are necessary for
the long-term conservation of the
subspecies, are already in place both as
a result of material provided on our Web
site and through public notice-andcomment procedures required to
establish the MSCP and specific subarea
plans.
In contrast to the lack of an
appreciable benefit of including these
lands as critical habitat, the exclusion of
these lands from critical habitat will
help preserve the partnerships that we
have developed with the local
jurisdictions and project proponents in
the development of the MSCP. As
discussed above, many landowners
perceive critical habitat as an unfair and
unnecessary regulatory burden given the
expense and time involved in
developing and implementing complex
regional HCPs, such as the MSCP. For
these reasons, we believe that
designating critical habitat has little
benefit in areas covered by the MSCP
subarea plans, and such minor benefit is
outweighed by the benefits of
maintaining partnerships with local
jurisdictions and private landowners
with lands covered by the MSCP.
We have reviewed and evaluated the
benefits of inclusion and the benefits of
exclusion of lands as critical habitat for
Acanthomintha ilicifolia. Based on this
evaluation, we find that the benefits of
excluding lands in the planning area for
the City of San Diego and the County of
San Diego subarea plans outweigh the
benefits of including those lands as
critical habitat for A. ilicifolia.
Exclusion Will Not Result in Extinction
of the Species
Exclusion of these 1,130 ac (457 ha)
of non-Federal lands from the final
designation of critical habitat will not
result in the extinction of
Acanthomintha ilicifolia because these
lands, determined to contain features
essential to the conservation of the
species, will be permanently conserved
and managed for the benefit of this
species pursuant to the approved MSCP
subarea plans. The jeopardy standard of
section 7 and routine implementation of
habitat protection through the section 7
process also provide assurances that the
species will not go extinct. The
protections afforded to A. ilicifolia
under the jeopardy standard will remain
in place for the areas proposed for
exclusion from critical habitat.
Economic Analysis
An analysis of the economic impacts
of proposing critical habitat for
Acanthomintha ilicifolia is being
prepared. We will announce the
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availability of the draft economic
analysis as soon as it is completed, at
which time we will seek public review
and comment. At that time, copies of
the draft economic analysis will be
available for downloading from the
Internet at https://www.fws.gov/carlsbad/
or by contacting the Carlsbad Fish and
Wildlife Office directly (see ADDRESSES
section). Based on public comments, the
proposed designation itself, and the
information in the full economic
analysis, areas in addition to those
proposed for exclusion in this proposed
rule may be excluded from final critical
habitat by the Secretary under the
provisions of section 4(b)(2) of the Act.
This is provided for in the Act and in
our implementing regulations at 50 CFR
424.19.
Peer Review
In accordance with our joint policy
published in the Federal Register on
July 1, 1994 (59 FR 34270), we will seek
the expert opinions of at least three
appropriate and independent specialists
regarding this proposed rule. The
purpose of such review is to ensure that
our critical habitat designation is based
on scientifically sound data,
assumptions, and analyses. We will
send these peer reviewers copies of this
proposed rule immediately following
publication in the Federal Register. We
will invite these peer reviewers to
comment, during the public comment
period, on the specific assumptions and
conclusions regarding the proposed
designation of critical habitat.
We will consider all comments and
information received during the
comment period on this proposed rule
during preparation of a final
rulemaking. Accordingly, the final
decision may differ from this proposal.
Public Hearings
The Act provides for one or more
public hearings on this proposal, if
requested. Requests for public hearings
must be made in writing at least 15 days
prior to the close of the public comment
period (see DATES section). We will
schedule public hearings on this
proposal, if any are requested, and
announce the dates, times, and places of
those hearings in the Federal Register
and local newspapers at least 15 days
prior to the first hearing.
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 rule easier to understand,
including answers to questions such as
the following: (1) Are the requirements
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in the proposed rule clearly stated? (2)
Does the proposed rule contain
technical jargon that interferes with the
clarity? (3) Does the format of the
proposed rule (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 of the preamble
helpful in understanding the proposed
rule? (5) What else could we do to make
this proposed rule easier to understand?
Send a copy of any comments on how
we could make this proposed rule 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.
cprice-sewell on PROD1PC66 with PROPOSALS2
Required Determinations
Regulatory Planning and Review
In accordance with Executive Order
12866, this document is a significant
rule in that it may raise novel legal and
policy issues, but it is not anticipated to
have an annual effect on the economy
of $100 million or more or affect the
economy in a material way. Due to the
tight timeline for publication in the
Federal Register, the Office of
Management and Budget (OMB) has not
formally reviewed this rule. We are
preparing a draft economic analysis of
this proposed action, which will be
available for public comment, to
determine the economic consequences
of designating the specific area as
critical habitat. This economic analysis
also will be used to determine
compliance with Executive Order
12866, Regulatory Flexibility Act, Small
Business Regulatory Enforcement
Fairness Act, and Executive Order
12630.
Further, Executive Order 12866
directs Federal Agencies promulgating
regulations to evaluate regulatory
alternatives (Office of Management and
Budget, Circular A–4, September 17,
2003). Pursuant to Circular A–4, once it
has been determined that the Federal
regulatory action is appropriate, then
the agency will need to consider
alternative regulatory approaches. Since
the determination of critical habitat is a
statutory requirement pursuant to the
Endangered Species Act of 1973, as
amended (Act) (16 U.S.C. 1531 et seq.),
we must then evaluate alternative
regulatory approaches, where feasible,
when promulgating a designation of
critical habitat.
In developing our designations of
critical habitat, we consider economic
impacts, impacts to national security,
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and other relevant impacts pursuant to
section 4(b)(2) of the Act. Based on the
discretion allowable under this
provision, we may exclude any
particular area from the designation of
critical habitat providing that the
benefits of such exclusion outweigh the
benefits of specifying the area as critical
habitat and that such exclusion would
not result in the extinction of the
subspecies. As such, we believe that the
evaluation of the inclusion or exclusion
of particular areas, or combination
thereof, in a designation constitutes our
regulatory alternative analysis.
The availability of the draft economic
analysis will be announced in the
Federal Register and in local
newspapers so that it is available for
public review and comments. The draft
economic analysis can be obtained from
the Internet Web site at https://
www.fws.gov/carlsbad/ or by contacting
the Carlsbad Fish and Wildlife Office
directly (see ADDRESSES section).
Regulatory Flexibility Act (5 U.S.C. 601
et seq.)
Under the Regulatory Flexibility Act
(5 U.S.C. 601 et seq., as amended by the
Small Business Regulatory Enforcement
Fairness Act (SBREFA) of 1996),
whenever an agency is required to
publish a notice of rulemaking for any
proposed or final rule, it must prepare
and make available for public comment
a regulatory flexibility analysis that
describes the effects of the rule on small
entities (i.e., small businesses, small
organizations, and small government
jurisdictions). However, no regulatory
flexibility analysis is required if the
head of the agency certifies the rule will
not have a significant economic impact
on a substantial number of small
entities. The SBREFA amended the
Regulatory Flexibility Act (RFA) to
require Federal agencies to provide a
statement of the factual basis for
certifying that the rule will not have a
significant economic impact on a
substantial number of small entities.
At this time, the Service lacks the
available economic information
necessary to provide an adequate factual
basis for the required RFA finding.
Therefore, the RFA finding is deferred
until completion of the draft economic
analysis prepared under section 4(b)(2)
of the Act and Executive Order 12866.
This draft economic analysis will
provide the required factual basis for the
RFA finding. Upon completion of the
draft economic analysis, the Service will
publish a notice of availability of the
draft economic analysis of the proposed
designation and reopen the public
comment period for the proposed
designation. The Service will include
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11965
with the notice of availability, as
appropriate, an initial regulatory
flexibility analysis or a certification that
the rule will not have a significant
economic impact on a substantial
number of small entities accompanied
by the factual basis for that
determination. The Service has
concluded that deferring the RFA
finding until completion of the draft
economic analysis is necessary to meet
the purposes and requirements of the
RFA. Deferring the RFA finding in this
manner will ensure that the Service
makes a sufficiently informed
determination based on adequate
economic information and provides the
necessary opportunity for public
comment.
Executive Order 13211
On May 18, 2001, the President issued
an Executive Order (E.O. 13211; Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use) on regulations that
significantly affect energy supply,
distribution, and use. Executive Order
13211 requires agencies to prepare
Statements of Energy Effects when
undertaking certain actions. While this
proposed rule to designate critical
habitat for Acanthomintha ilicifolia is a
significant regulatory action under
Executive Order 12866, in that it may
raise novel legal and policy issues, it is
not expected to significantly affect
energy supplies, distribution, or use.
Therefore, this action is not a significant
energy action and no Statement of
Energy Effects is required.
Unfunded Mandates Reform Act (2
U.S.C. 1501 et seq.)
In accordance with the Unfunded
Mandates Reform Act (2 U.S.C. 1501),
the Service makes the following
findings:
(a) This rule will not produce a
Federal mandate. In general, a Federal
mandate is a provision in legislation,
statute or regulation that would impose
an enforceable duty upon State, local,
Tribal governments, or the private sector
and includes both ‘‘Federal
intergovernmental mandates’’ and
‘‘Federal private sector mandates.’’
These terms are defined in 2 U.S.C.
658(5)–(7). ‘‘Federal intergovernmental
mandate’’ includes a regulation that
‘‘would impose an enforceable duty
upon State, local, or Tribal
governments’’ with two exceptions. It
excludes ‘‘a condition of Federal
assistance.’’ It also excludes ‘‘a duty
arising from participation in a voluntary
Federal program,’’ unless the regulation
‘‘relates to a then-existing Federal
program under which $500,000,000 or
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more is provided annually to State,
local, and Tribal governments under
entitlement authority,’’ if the provision
would ‘‘increase the stringency of
conditions of assistance’’ or ‘‘place caps
upon, or otherwise decrease, the Federal
Government’s responsibility to provide
funding,’’ and the State, local, or Tribal
governments ‘‘lack authority’’ to adjust
accordingly. At the time of enactment,
these entitlement programs were:
Medicaid; AFDC work programs; Child
Nutrition; Food Stamps; Social Services
Block Grants; Vocational Rehabilitation
State Grants; Foster Care, Adoption
Assistance, and Independent Living;
Family Support Welfare Services; and
Child Support Enforcement. ‘‘Federal
private sector mandate’’ includes a
regulation that ‘‘would impose an
enforceable duty upon the private
sector, except (i) a condition of Federal
assistance or (ii) a duty arising from
participation in a voluntary Federal
program.’’
The designation of critical habitat
does not impose a legally binding duty
on non-Federal Government entities or
private parties. Under the Act, the only
regulatory effect is that Federal agencies
must ensure that their actions do not
destroy or adversely modify critical
habitat under section 7. While nonFederal entities that receive Federal
funding, assistance, or permits, or that
otherwise require approval or
authorization from a Federal agency for
an action, may be indirectly impacted
by the designation of critical habitat, the
legally binding duty to avoid
destruction or adverse modification of
critical habitat rests squarely on the
Federal agency. Furthermore, to the
extent that non-Federal entities are
indirectly impacted because they
receive Federal assistance or participate
in a voluntary Federal aid program, the
Unfunded Mandates Reform Act would
not apply; nor would critical habitat
shift the costs of the large entitlement
programs listed above on to State
governments.
(b) We do not believe that this rule
will significantly or uniquely affect
small governments because 91 percent
of the lands being proposed for final
designation are managed by Federal
agencies and do not fit the definition of
‘‘small governmental jurisdiction.’’ As
such, a Small Government Agency Plan
is not required. We will, however,
further evaluate this issue as we
conduct our economic analysis and
revise this assessment if appropriate.
Takings
In accordance with Executive Order
12630 (‘‘Government Actions and
Interference with Constitutionally
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Protected Private Property Rights’’), we
have analyzed the potential takings
implications of designating critical
habitat for Acanthomintha ilicifolia in a
takings implications assessment. The
takings implications assessment
concludes that this designation of
critical habitat for the A. ilicifolia does
not pose significant takings
implications.
Federalism
In accordance with Executive Order
13132 (Federalism), the rule does not
have significant Federalism effects. A
Federalism assessment is not required.
In keeping with Department of the
Interior and Department of Commerce
policy, we requested information from,
and coordinated development of, this
proposed critical habitat designation
with appropriate State resource agencies
in California. The designation of critical
habitat in areas currently occupied by
Acanthomintha ilicifolia imposes no
additional restrictions to those currently
in place and, therefore, has little
incremental impact on State and local
governments and their activities. The
designation may have some benefit to
these governments in that the areas that
contain the features essential to the
conservation of the species are more
clearly defined, and the primary
constituent elements of the habitat
necessary to the conservation of the
species are specifically identified. While
making this definition and
identification does not alter where and
what federally sponsored activities may
occur, it may assist these local
governments in long-range planning
(rather than waiting for case-by-case
section 7 consultations to occur).
Civil Justice Reform
In accordance with Executive Order
12988, the Office of the Solicitor has
determined that the rule does not
unduly burden the judicial system and
meets the requirements of sections 3(a)
and 3(b)(2) of the Order. We have
proposed designating critical habitat in
accordance with the provisions of the
Act. This proposed rule uses standard
property descriptions and identifies the
primary constituent elements within the
designated areas to assist the public in
understanding the habitat needs of
Acanthomintha ilicifolia.
Paperwork Reduction Act of 1995 (44
U.S.C. 3501 et seq.)
This rule does not contain any new
collections of information that require
approval by OMB under the Paperwork
Reduction Act. This rule will not
impose recordkeeping or reporting
requirements on State or local
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Fmt 4701
Sfmt 4702
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
jurisdiction of the Tenth Federal Circuit
Court, 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 that were occupied at the time of
listing that contain features essential for
the conservation of Acanthomintha
ilicifolia and no Tribal lands essential
for the conservation of A. ilicifolia.
Therefore, critical habitat for A. ilicifolia
has not been proposed on Tribal lands.
References Cited
A complete list of all references cited
in this rulemaking is available upon
request from the Field Supervisor,
Carlsbad Fish and Wildlife Office (see
ADDRESSES section).
Author(s)
The primary author of this package is
the Carlsbad Fish and Wildlife Office.
List of Subjects in 50 CFR Part 17
Endangered and threatened species,
Exports, Imports, Reporting and
recordkeeping requirements,
Transportation.
Proposed Regulation Promulgation
Accordingly, we propose to amend
part 17, subchapter B of chapter I, title
50 of the Code of Federal Regulations,
as set forth below:
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Authority: 16 U.S.C. 1361–1407; 16 U.S.C.
1531–1544; 16 U.S.C. 4201–4245; Pub. L. 99–
625, 100 Stat. 3500; unless otherwise noted.
PART 17—[AMENDED]
1. The authority citation for part 17
continues to read as follows:
2. In § 17.12(h), revise the entry for
‘‘Acanthomintha ilicifolia’’ under
‘‘FLOWERING PLANTS’’ to read as
follows:
§ 17.12
*
Endangered and threatened plants.
*
*
(h) * * *
*
Species
Historic range
Scientific name
Family
Status
*
U.S.A. (CA), Mexico
*
Lamiaceae ..............
When listed
Common name
*
Critical
habitat
Special
rules
FLOWERING PLANTS
*
Acanthomintha
ilicifolia.
*
San Diego thornmint
*
*
*
3. Amend § 17.96(a) by adding an
entry for ‘‘Acanthomintha ilicifolia (San
Diego thornmint)’’ in alphabetical order
under family Lamiaceae, to read as
follows:
§ 17.96
Critical habitat—plants..
(a) Flowering plants.
*
*
*
*
*
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Family Lamiaceae: Acanthomintha
ilicifolia (San Diego thornmint)
(1) Critical habitat units are depicted
for San Diego County, California, on the
maps below.
(2) The primary constituent element
of critical habitat for Acanthomintha
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*
649
*
*
*
T
*
ilicifolia is clay lenses that provide
substrate for seedling establishment and
space for growth and development of
Acanthomintha ilicifolia, that are:
(i) Within chaparral and coastal sage
scrub;
(ii) On gentle slopes ranging from 0 to
25 degrees;
(iii) Derived from gabbro and soft
calcareous sandstone substrates with a
loose, crumbly structure and deep
(approximately 2 feet (60 cm)) fissures;
and
(iv) Characterized by a low density of
forbs and geophytes, and a low density
or absence of shrubs.
PO 00000
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*
17.96(a)
NA
*
(3) Critical habitat does not include
manmade structures (such as buildings,
aqueducts, airports, and roads) and the
land on which such structures are
located existing on the effective date of
this rule.
(4) Data layers defining map units
were created on a base of USGS 1:24,000
maps, and critical habitat units were
then mapped using Universal
Transverse Mercator (UTM) coordinates.
(5) Note: Index map for
Acanthomintha ilicifolia (Map 1)
follows:
BILLING CODE 4310–55–P
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BILLING CODE 4310–55–C
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(6) Unit 1: San Diego County,
California. From USGS 1:24,000
quadrangle maps Encinitas, Rancho
Santa Fe, and San Luis Rey.
(i) Subunit 1A. Land bounded by the
following UTM NAD27 coordinates
(E,N): 475096, 3665684; 475097,
3665687; 475098, 3665697; 475100,
3665707; 475103, 3665716; 475107,
3665725; 475111, 3665735; 475114,
3665741; 475123, 3665756; 475124,
3665759; 475129, 3665767; 475135,
3665775; 475142, 3665783; 475148,
3665790; 475156, 3665797; 475161,
3665801; 475175, 3665813; 475178,
3665815; 475186, 3665821; 475195,
3665826; 475203, 3665831; 475212,
3665835; 475215, 3665836; 475216,
3665844; 475216, 3665854; 475218,
3665864; 475220, 3665873; 475223,
3665883; 475227, 3665892; 475231,
3665901; 475236, 3665910; 475241,
3665919; 475247, 3665927; 475253,
3665934; 475260, 3665942; 475267,
3665948; 475286, 3665965; 475286,
3665965; 475294, 3665972; 475302,
3665977; 475310, 3665983; 475319,
3665987; 475328, 3665991; 475337,
3665995; 475338, 3665995; 475372,
3666006; 475381, 3666009; 475390,
3666011; 475400, 3666013; 475410,
3666014; 475420, 3666014; 475430,
3666014; 475440, 3666013; 475450,
3666011; 475452, 3666011; 475478,
3666005; 475474, 3666011; 475472,
3666014; 475466, 3666022; 475461,
3666030; 475456, 3666039; 475452,
3666048; 475448, 3666057; 475445,
3666067; 475443, 3666077; 475441,
3666087; 475440, 3666096; 475440,
3666106; 475440, 3666116; 475441,
3666126; 475443, 3666134; 475446,
3666150; 475446, 3666152; 475448,
3666162; 475451, 3666171; 475455,
3666181; 475459, 3666190; 475464,
3666199; 475468, 3666205; 475479,
3666223; 475480, 3666225; 475486,
3666233; 475492, 3666241; 475496,
3666245; 475511, 3666260; 475514,
3666263; 475518, 3666267; 475517,
3666269; 475517, 3666272; 475517,
3666275; 475516, 3666278; 475516,
3666281; 475516, 3666284; 475516,
3666287; 475516, 3666289; 475516,
3666292; 475516, 3666295; 475516,
3666298; 475517, 3666301; 475517,
3666304; 475517, 3666307; 475518,
3666310; 475518, 3666313; 475519,
3666315; 475519, 3666318; 475520,
3666321; 475520, 3666324; 475521,
3666327; 475522, 3666330; 475523,
3666332; 475524, 3666335; 475524,
3666338; 475525, 3666341; 475526,
3666343; 475528, 3666346; 475529,
3666349; 475530, 3666351; 475531,
3666354; 475532, 3666357; 475534,
3666359; 475535, 3666362; 475536,
3666364; 475538, 3666367; 475539,
VerDate Aug<31>2005
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Jkt 211001
3666369; 475541, 3666372; 475543,
3666374; 475544, 3666376; 475546,
3666379; 475548, 3666381; 475550,
3666383; 475551, 3666386; 475553,
3666388; 475555, 3666390; 475557,
3666392; 475559, 3666394; 475561,
3666396; 475563, 3666398; 475565,
3666400; 475568, 3666402; 475570,
3666404; 475572, 3666406; 475574,
3666408; 475577, 3666410; 475579,
3666411; 475581, 3666413; 475584,
3666415; 475586, 3666416; 475589,
3666418; 475591, 3666419; 475594,
3666421; 475596, 3666422; 475599,
3666424; 475601, 3666425; 475604,
3666426; 475607, 3666427; 475609,
3666428; 475612, 3666430; 475615,
3666431; 475617, 3666432; 475620,
3666433; 475623, 3666433; 475626,
3666434; 475628, 3666435; 475631,
3666436; 475634, 3666437; 475637,
3666437; 475640, 3666438; 475643,
3666438; 475645, 3666439; 475648,
3666439; 475651, 3666439; 475654,
3666440; 475657, 3666440; 475660,
3666440; 475663, 3666440; 475666,
3666440; 475669, 3666440; 475671,
3666440; 475674, 3666440; 475677,
3666440; 475680, 3666440; 475683,
3666440; 475686, 3666439; 475689,
3666439; 475692, 3666439; 475695,
3666438; 475697, 3666438; 475700,
3666437; 475703, 3666437; 475706,
3666436; 475709, 3666435; 475712,
3666434; 475714, 3666433; 475717,
3666433; 475720, 3666432; 475723,
3666431; 475725, 3666430; 475728,
3666428; 475731, 3666427; 475733,
3666426; 475736, 3666425; 475738,
3666424; 475741, 3666422; 475744,
3666421; 475746, 3666419; 475749,
3666418; 475751, 3666416; 475753,
3666415; 475756, 3666413; 475758,
3666411; 475761, 3666410; 475763,
3666408; 475765, 3666406; 475767,
3666404; 475770, 3666402; 475772,
3666400; 475774, 3666398; 475776,
3666396; 475778, 3666394; 475780,
3666392; 475782, 3666390; 475784,
3666388; 475786, 3666386; 475788,
3666383; 475789, 3666381; 475791,
3666379; 475793, 3666376; 475794,
3666374; 475796, 3666372; 475798,
3666369; 475799, 3666367; 475801,
3666364; 475802, 3666362; 475803,
3666359; 475805, 3666357; 475806,
3666354; 475807, 3666351; 475808,
3666349; 475810, 3666346; 475811,
3666343; 475812, 3666341; 475813,
3666338; 475814, 3666335; 475814,
3666332; 475815, 3666330; 475816,
3666327; 475817, 3666324; 475817,
3666321; 475818, 3666318; 475819,
3666315; 475819, 3666313; 475820,
3666310; 475820, 3666307; 475820,
3666304; 475820, 3666301; 475821,
3666298; 475821, 3666295; 475821,
3666292; 475821, 3666289; 475821,
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11969
3666287; 475821, 3666284; 475821,
3666281; 475821, 3666278; 475820,
3666275; 475820, 3666272; 475820,
3666269; 475820, 3666266; 475819,
3666263; 475819, 3666261; 475818,
3666258; 475817, 3666255; 475817,
3666252; 475816, 3666249; 475815,
3666246; 475814, 3666244; 475814,
3666241; 475813, 3666238; 475812,
3666235; 475811, 3666233; 475810,
3666230; 475808, 3666227; 475807,
3666225; 475806, 3666222; 475806,
3666222; 475810, 3666213; 475814,
3666204; 475818, 3666195; 475821,
3666185; 475823, 3666176; 475825,
3666166; 475825, 3666166; 475828,
3666141; 475829, 3666132; 475829,
3666122; 475829, 3666118; 475791,
3666114; 475770, 3666086; 475762,
3666044; 475760, 3666013; 475747,
3665994; 475743, 3665966; 475740,
3665964; 475734, 3665961; 475718,
3665953; 475714, 3665951; 475705,
3665947; 475697, 3665944; 475678,
3665937; 475677, 3665937; 475667,
3665934; 475657, 3665931; 475647,
3665930; 475638, 3665929; 475628,
3665928; 475627, 3665928; 475628,
3665928; 475633, 3665924; 475640,
3665918; 475648, 3665911; 475655,
3665904; 475656, 3665902; 475656,
3665902; 475659, 3665900; 475661,
3665899; 475663, 3665897; 475666,
3665895; 475668, 3665893; 475670,
3665892; 475673, 3665890; 475675,
3665888; 475677, 3665886; 475679,
3665884; 475681, 3665882; 475683,
3665880; 475685, 3665878; 475687,
3665876; 475689, 3665873; 475691,
3665871; 475693, 3665869; 475695,
3665867; 475696, 3665864; 475698,
3665862; 475700, 3665860; 475701,
3665857; 475703, 3665855; 475704,
3665852; 475706, 3665850; 475707,
3665847; 475709, 3665845; 475710,
3665842; 475711, 3665840; 475713,
3665837; 475714, 3665834; 475715,
3665832; 475716, 3665829; 475717,
3665826; 475718, 3665823; 475719,
3665821; 475720, 3665818; 475721,
3665815; 475721, 3665812; 475722,
3665809; 475723, 3665807; 475723,
3665804; 475724, 3665801; 475724,
3665798; 475725, 3665795; 475725,
3665792; 475726, 3665789; 475726,
3665787; 475726, 3665784; 475726,
3665781; 475726, 3665778; 475726,
3665775; 475726, 3665772; 475726,
3665769; 475726, 3665766; 475726,
3665763; 475726, 3665760; 475726,
3665758; 475725, 3665755; 475725,
3665752; 475724, 3665749; 475724,
3665746; 475723, 3665743; 475723,
3665740; 475722, 3665738; 475721,
3665735; 475721, 3665732; 475720,
3665729; 475719, 3665726; 475718,
3665724; 475717, 3665721; 475716,
3665718; 475715, 3665715; 475714,
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3665713; 475713, 3665710; 475711,
3665708; 475710, 3665705; 475709,
3665702; 475707, 3665700; 475706,
3665697; 475704, 3665695; 475703,
3665692; 475701, 3665690; 475700,
3665687; 475698, 3665685; 475696,
3665683; 475695, 3665680; 475693,
3665678; 475691, 3665676; 475689,
3665674; 475687, 3665671; 475685,
3665669; 475683, 3665667; 475681,
3665665; 475679, 3665663; 475677,
3665661; 475675, 3665659; 475673,
3665657; 475670, 3665655; 475668,
3665654; 475666, 3665652; 475663,
3665650; 475661, 3665648; 475659,
3665647; 475656, 3665645; 475654,
3665644; 475651, 3665642; 475649,
3665641; 475646, 3665639; 475644,
3665638; 475641, 3665637; 475639,
3665635; 475636, 3665634; 475633,
3665633; 475631, 3665632; 475628,
3665631; 475625, 3665630; 475622,
3665629; 475620, 3665628; 475617,
3665627; 475614, 3665626; 475611,
3665626; 475611, 3665626; 475606,
3665623; 475592, 3665616; 475588,
3665614; 475579, 3665609; 475570,
3665606; 475560, 3665603; 475550,
3665601; 475541, 3665599; 475531,
3665598; 475521, 3665598; 475516,
3665598; 475499, 3665598; 475493,
3665599; 475483, 3665600; 475483,
3665600; 475478, 3665591; 475473,
3665583; 475473, 3665582; 475461,
3665565; 475332, 3665536; 475214,
3665515; 475174, 3665573; 475133,
3665640; 475096, 3665684.
(ii) Subunit 1B. Land bounded by the
following UTM NAD27 coordinates
(E,N): 478577, 3658061; 478502,
3658045; 478459, 3658073; 478427,
3658140; 478414, 3658174; 478412,
3658184; 478404, 3658287; 478398,
3658413; 478379, 3658480; 478359,
3658505; 478318, 3658541; 478295,
3658577; 478287, 3658598; 478293,
3658651; 478292, 3658653; 478293,
3658655; 478304, 3658664; 478362,
3658678; 478421, 3658675; 478419,
3658657; 478490, 3658561; 478577,
3658547; 478607, 3658546; 478607,
3658545; 478607, 3658544; 478622,
3658547; 478643, 3658450; 478613,
3658445; 478558, 3658434; 478496,
3658417; 478433, 3658380; 478425,
3658352; 478433, 3658312; 478462,
3658276; 478495, 3658238; 478496,
3658193; 478517, 3658165; 478539,
3658153; 478570, 3658154; 478610,
3658193; 478653, 3658233; 478687,
3658246; 478725, 3658269; 478751,
3658293; 478780, 3658310; 478814,
3658329; 478872, 3658327; 478909,
3658307; 478983, 3658336; 479014,
3658346; 479049, 3658356; 479090,
3658352; 479135, 3658332; 479149,
3658331; 479153, 3658322; 479162,
3658278; 479162, 3658253; 479153,
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
3658203; 479145, 3658182; 478916,
3658114; 478847, 3658113; 478797,
3658086; 478775, 3658055; 478783,
3658021; 478835, 3657960; 478913,
3657958; 478951, 3657952; 479038,
3657957; 479174, 3658048; 479210,
3658055; 479218, 3658005; 479227,
3657890; 479221, 3657887; 479175,
3657833; 479114, 3657784; 479078,
3657769; 479078, 3657768; 479069,
3657770; 479059, 3657773; 479050,
3657776; 479041, 3657780; 479032,
3657785; 479024, 3657790; 479016,
3657796; 479008, 3657802; 479001,
3657809; 478995, 3657815; 478995,
3657815; 478993, 3657813; 478990,
3657812; 478988, 3657810; 478985,
3657808; 478983, 3657807; 478980,
3657805; 478978, 3657804; 478975,
3657802; 478973, 3657801; 478970,
3657800; 478968, 3657799; 478965,
3657797; 478962, 3657796; 478960,
3657795; 478957, 3657794; 478954,
3657793; 478951, 3657792; 478949,
3657791; 478946, 3657790; 478943,
3657790; 478940, 3657789; 478937,
3657788; 478935, 3657787; 478932,
3657787; 478929, 3657786; 478926,
3657786; 478923, 3657786; 478920,
3657785; 478917, 3657785; 478915,
3657785; 478912, 3657784; 478909,
3657784; 478906, 3657784; 478903,
3657784; 478900, 3657784; 478897,
3657784; 478894, 3657784; 478891,
3657785; 478888, 3657785; 478886,
3657785; 478883, 3657786; 478880,
3657786; 478877, 3657786; 478874,
3657787; 478871, 3657787; 478868,
3657788; 478866, 3657789; 478863,
3657790; 478861, 3657790; 478839,
3657880; 478789, 3657835; 478788,
3657836; 478786, 3657835; 478783,
3657834; 478780, 3657833; 478777,
3657833; 478775, 3657832; 478772,
3657831; 478769, 3657831; 478766,
3657830; 478763, 3657829; 478760,
3657829; 478757, 3657829; 478755,
3657828; 478752, 3657828; 478749,
3657828; 478746, 3657827; 478743,
3657827; 478740, 3657827; 478737,
3657827; 478734, 3657827; 478731,
3657827; 478728, 3657827; 478726,
3657828; 478723, 3657828; 478720,
3657828; 478717, 3657829; 478714,
3657829; 478679, 3657945; 478657,
3658051; 478657, 3658070; 478599,
3658060; 478577, 3658061.
(iii) Subunit 1C. Land bounded by the
following UTM NAD27 coordinates
(E,N): 476907, 3654254; 476907,
3654250; 476907, 3654240; 476906,
3654238; 476883, 3654238; 476860,
3654220; 476860, 3654195; 476892,
3654171; 476889, 3654164; 476885,
3654155; 476882, 3654150; 476881,
3654148; 476867, 3654148; 476850,
3654104; 476850, 3654102; 476848,
3654099; 476841, 3654092; 476834,
PO 00000
Frm 00026
Fmt 4701
Sfmt 4702
3654086; 476824, 3654076; 476823,
3654076; 476815, 3654069; 476807,
3654063; 476803, 3654061; 476791,
3654053; 476787, 3654051; 476783,
3654049; 476783, 3654056; 476783,
3654075; 476777, 3654098; 476756,
3654100; 476732, 3654111; 476726,
3654119; 476730, 3654144; 476743,
3654174; 476760, 3654207; 476781,
3654239; 476810, 3654262; 476819,
3654295; 476814, 3654339; 476789,
3654350; 476753, 3654337; 476753,
3654314; 476730, 3654283; 476699,
3654259; 476670, 3654230; 476667,
3654190; 476649, 3654157; 476623,
3654152; 476579, 3654152; 476539,
3654155; 476491, 3654153; 476468,
3654148; 476467, 3654151; 476463,
3654160; 476462, 3654162; 476457,
3654175; 476454, 3654182; 476451,
3654192; 476449, 3654200; 476446,
3654214; 476446, 3654215; 476445,
3654222; 476510, 3654211; 476554,
3654209; 476581, 3654228; 476586,
3654259; 476577, 3654287; 476519,
3654289; 476485, 3654306; 476451,
3654315; 476452, 3654320; 476457,
3654334; 476457, 3654335; 476461,
3654344; 476465, 3654353; 476467,
3654358; 476474, 3654370; 476476,
3654374; 476481, 3654383; 476487,
3654391; 476488, 3654392; 476497,
3654403; 476502, 3654409; 476509,
3654417; 476515, 3654423; 476519,
3654426; 476609, 3654448; 476623,
3654488; 476612, 3654894; 476622,
3654895; 476626, 3654895; 476636,
3654894; 476646, 3654893; 476648,
3654893; 476662, 3654891; 476670,
3654890; 476680, 3654888; 476688,
3654885; 476701, 3654881; 476702,
3654880; 476712, 3654877; 476721,
3654873; 476726, 3654870; 476738,
3654864; 476742, 3654861; 476750,
3654856; 476753, 3654854; 476753,
3654854; 476756, 3654856; 476758,
3654857; 476761, 3654858; 476764,
3654860; 476766, 3654861; 476769,
3654862; 476772, 3654863; 476774,
3654864; 476777, 3654865; 476780,
3654866; 476783, 3654867; 476785,
3654868; 476788, 3654868; 476787,
3654872; 476787, 3654882; 476787,
3654892; 476788, 3654901; 476790,
3654911; 476792, 3654921; 476795,
3654931; 476797, 3654935; 476798,
3654942; 476800, 3654952; 476803,
3654961; 476807, 3654971; 476811,
3654980; 476815, 3654989; 476821,
3654997; 476826, 3655005; 476833,
3655013; 476840, 3655020; 476847,
3655027; 476855, 3655033; 476863,
3655039; 476871, 3655044; 476880,
3655049; 476889, 3655053; 476893,
3655055; 476901, 3655058; 476906,
3655060; 476916, 3655063; 476926,
3655065; 476935, 3655067; 476945,
3655067; 476955, 3655068; 476965,
E:\FR\FM\14MRP2.SGM
14MRP2
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
cprice-sewell on PROD1PC66 with PROPOSALS2
3655067; 476975, 3655067; 476985,
3655065; 476995, 3655063; 477004,
3655060; 477014, 3655056; 477023,
3655052; 477028, 3655049; 477034,
3655046; 477037, 3655044; 477045,
3655039; 477054, 3655033; 477061,
3655027; 477069, 3655020; 477075,
3655013; 477082, 3655005; 477088,
3654997; 477093, 3654989; 477098,
3654980; 477102, 3654971; 477105,
3654961; 477108, 3654952; 477109,
3654947; 477112, 3654936; 477113,
3654932; 477114, 3654925; 477114,
3654924; 477118, 3654915; 477121,
3654905; 477123, 3654896; 477125,
3654886; 477126, 3654876; 477126,
3654866; 477126, 3654856; 477125,
3654846; 477123, 3654836; 477121,
3654826; 477118, 3654817; 477114,
3654807; 477110, 3654798; 477105,
3654790; 477100, 3654781; 477094,
3654773; 477088, 3654765; 477081,
3654758; 477074, 3654751; 477066,
3654745; 477058, 3654739; 477050,
3654734; 477045, 3654731; 477038,
3654727; 477035, 3654726; 477027,
3654722; 477018, 3654718; 477009,
3654714; 477008, 3654714; 477008,
3654712; 477009, 3654709; 477010,
3654706; 477010, 3654703; 477011,
3654700; 477012, 3654697; 477012,
3654695; 477012, 3654692; 477013,
3654689; 477013, 3654686; 477013,
3654683; 477014, 3654680; 477014,
3654677; 477014, 3654674; 477014,
3654671; 477014, 3654669; 477014,
3654666; 477014, 3654663; 477014,
3654660; 477013, 3654657; 477013,
3654654; 477013, 3654651; 477012,
3654648; 477012, 3654645; 477012,
3654643; 477011, 3654640; 477010,
3654637; 477010, 3654634; 477009,
3654631; 477008, 3654628; 477007,
3654626; 477007, 3654623; 477006,
3654620; 477005, 3654617; 477004,
3654615; 477003, 3654612; 477001,
3654609; 477000, 3654607; 476999,
3654604; 476998, 3654601; 476996,
3654599; 476995, 3654596; 476994,
3654594; 476992, 3654591; 476991,
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
3654589; 476989, 3654586; 476987,
3654584; 476986, 3654582; 476984,
3654579; 476982, 3654577; 476981,
3654575; 476979, 3654572; 476977,
3654570; 476975, 3654568; 476973,
3654566; 476971, 3654564; 476969,
3654562; 476967, 3654560; 476965,
3654558; 476963, 3654556; 476960,
3654554; 476958, 3654552; 476956,
3654550; 476954, 3654548; 476951,
3654547; 476949, 3654545; 476951,
3654545; 476953, 3654546; 476956,
3654546; 476959, 3654546; 476962,
3654547; 476965, 3654547; 476968,
3654547; 476971, 3654547; 476974,
3654547; 476977, 3654547; 476979,
3654547; 476982, 3654547; 476985,
3654547; 476988, 3654546; 476991,
3654546; 476994, 3654546; 476997,
3654545; 477000, 3654545; 477003,
3654544; 477005, 3654544; 477008,
3654543; 477011, 3654542; 477014,
3654542; 477017, 3654541; 477019,
3654540; 477022, 3654539; 477025,
3654538; 477028, 3654537; 477030,
3654536; 477033, 3654535; 477036,
3654534; 477038, 3654533; 477041,
3654531; 477044, 3654530; 477046,
3654529; 477049, 3654527; 477051,
3654526; 477054, 3654524; 477056,
3654523; 477059, 3654521; 477061,
3654520; 477063, 3654518; 477066,
3654516; 477068, 3654514; 477070,
3654513; 477072, 3654511; 477075,
3654509; 477077, 3654507; 477079,
3654505; 477081, 3654503; 477083,
3654501; 477085, 3654499; 477087,
3654497; 477089, 3654494; 477091,
3654492; 477093, 3654490; 477094,
3654488; 477096, 3654485; 477098,
3654483; 477100, 3654481; 477101,
3654478; 477103, 3654476; 477104,
3654473; 477106, 3654471; 477107,
3654468; 477109, 3654466; 477110,
3654463; 477111, 3654461; 477112,
3654458; 477114, 3654455; 477115,
3654453; 477116, 3654450; 477117,
3654447; 477118, 3654444; 477119,
3654442; 477120, 3654439; 477120,
3654436; 477121, 3654433; 477122,
PO 00000
Frm 00027
Fmt 4701
Sfmt 4702
11971
3654431; 477123, 3654428; 477123,
3654425; 477124, 3654422; 477124,
3654419; 477125, 3654416; 477125,
3654413; 477125, 3654411; 477126,
3654408; 477126, 3654405; 477126,
3654402; 477126, 3654399; 477126,
3654396; 477126, 3654393; 477126,
3654390; 477126, 3654387; 477126,
3654384; 477126, 3654382; 477125,
3654379; 477125, 3654376; 477125,
3654373; 477124, 3654370; 477124,
3654367; 477123, 3654364; 477123,
3654361; 477122, 3654359; 477121,
3654356; 477120, 3654353; 477120,
3654350; 477119, 3654347; 477118,
3654345; 477117, 3654342; 477116,
3654339; 477115, 3654337; 477114,
3654334; 477112, 3654331; 477111,
3654329; 477110, 3654326; 477109,
3654323; 477107, 3654321; 477106,
3654318; 477104, 3654316; 477103,
3654313; 477101, 3654311; 477100,
3654308; 477098, 3654306; 477096,
3654304; 477094, 3654301; 477093,
3654299; 477091, 3654297; 477089,
3654295; 477087, 3654293; 477085,
3654290; 477083, 3654288; 477081,
3654286; 477079, 3654284; 477077,
3654282; 477075, 3654280; 477072,
3654278; 477070, 3654277; 477068,
3654275; 477066, 3654273; 477063,
3654271; 477061, 3654270; 477059,
3654268; 477056, 3654266; 477054,
3654265; 477051, 3654263; 477049,
3654262; 477046, 3654260; 477044,
3654259; 477041, 3654258; 477038,
3654256; 477036, 3654255; 477033,
3654254; 477030, 3654253; 477028,
3654252; 477025, 3654251; 477022,
3654250; 477019, 3654249; 477017,
3654248; 477015, 3654248; 477020,
3654362; 476951, 3654356; 476926,
3654345; 476896, 3654335; 476875,
3654322; 476869, 3654295; 476888,
3654268; 476907, 3654254.
(iv) Note: Map of Unit 1, subunits 1A,
1B, and 1C (Map 2), follows:
BILLING CODE 4310–55–P
E:\FR\FM\14MRP2.SGM
14MRP2
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
BILLING CODE 4310–55–C
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
PO 00000
Frm 00028
Fmt 4701
Sfmt 4702
E:\FR\FM\14MRP2.SGM
14MRP2
EP14MR07.001
cprice-sewell on PROD1PC66 with PROPOSALS2
11972
cprice-sewell on PROD1PC66 with PROPOSALS2
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
(7) Unit 2: San Diego County,
California. From USGS 1:24,000
quadrangle maps Del Mar, Poway, and
San Vicente Reservoir.
(i) Subunit 2A. Land bounded by the
following UTM NAD27 coordinates
(E,N): 483318, 3643315; 483328,
3643314; 483335, 3643313; 483349,
3643310; 483352, 3643310; 483362,
3643307; 483372, 3643304; 483381,
3643301; 483390, 3643297; 483395,
3643294; 483399, 3643292; 483402,
3643290; 483411, 3643285; 483419,
3643279; 483425, 3643274; 483438,
3643264; 483439, 3643262; 483447,
3643255; 483454, 3643248; 483460,
3643240; 483466, 3643232; 483466,
3643232; 483474, 3643220; 483479,
3643212; 483481, 3643208; 483489,
3643192; 483492, 3643188; 483496,
3643179; 483499, 3643171; 483504,
3643156; 483508, 3643147; 483510,
3643139; 483513, 3643130; 483515,
3643120; 483516, 3643120; 483519,
3643103; 483520, 3643093; 483521,
3643083; 483522, 3643073; 483522,
3643070; 483522, 3643058; 483521,
3643052; 483520, 3643042; 483519,
3643032; 483518, 3643030; 483515,
3643014; 483513, 3643006; 483510,
3642997; 483507, 3642987; 483506,
3642986; 483496, 3642962; 483492,
3642954; 483490, 3642949; 483487,
3642943; 483485, 3642939; 483476,
3642922; 483473, 3642917; 483472,
3642914; 483465, 3642904; 483462,
3642898; 483459, 3642895; 483456,
3642890; 483450, 3642882; 483450,
3642881; 483448, 3642878; 483447,
3642875; 483446, 3642873; 483444,
3642870; 483443, 3642868; 483441,
3642865; 483440, 3642863; 483438,
3642860; 483436, 3642858; 483435,
3642856; 483433, 3642853; 483431,
3642851; 483429, 3642849; 483427,
3642847; 483426, 3642845; 483423,
3642840; 483416, 3642833; 483415,
3642831; 483408, 3642823; 483402,
3642817; 483395, 3642810; 483390,
3642806; 483383, 3642800; 483380,
3642798; 483371, 3642792; 483363,
3642787; 483355, 3642783; 483336,
3642773; 483335, 3642772; 483326,
3642768; 483317, 3642765; 483307,
3642762; 483297, 3642760; 483288,
3642758; 483278, 3642757; 483273,
3642757; 483255, 3642756; 483249,
3642756; 483249, 3642756; 483235,
3642756; 483225, 3642756; 483215,
3642757; 483206, 3642759; 483202,
3642760; 483191, 3642762; 483186,
3642763; 483181, 3642764; 483172,
3642766; 483164, 3642768; 483150,
3642773; 483148, 3642773; 483139,
3642777; 483130, 3642781; 483121,
3642786; 483112, 3642791; 483110,
3642792; 483101, 3642799; 483095,
3642803; 483087, 3642809; 483082,
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
3642815; 483073, 3642824; 483072,
3642824; 483070, 3642826; 483061,
3642835; 483060, 3642836; 483053,
3642843; 483051, 3642846; 483042,
3642856; 483038, 3642861; 483032,
3642869; 483030, 3642872; 483021,
3642887; 483018, 3642893; 483015,
3642898; 483011, 3642904; 483009,
3642908; 483005, 3642917; 483003,
3642923; 483002, 3642924; 482998,
3642931; 482993, 3642939; 482992,
3642940; 482987, 3642948; 482983,
3642954; 482980, 3642959; 482979,
3642961; 482974, 3642970; 482970,
3642979; 482968, 3642983; 482963,
3642998; 482961, 3643001; 482960,
3643006; 482957, 3643012; 482955,
3643018; 482954, 3643020; 482952,
3643025; 482948, 3643036; 482946,
3643040; 482944, 3643049; 482942,
3643057; 482942, 3643057; 482941,
3643058; 482938, 3643068; 482936,
3643078; 482935, 3643087; 482934,
3643097; 482933, 3643107; 482933,
3643110; 482933, 3643120; 482934,
3643127; 482935, 3643137; 482936,
3643147; 482938, 3643156; 482940,
3643161; 482940, 3643162; 482943,
3643171; 482946, 3643181; 482950,
3643190; 482955, 3643199; 482960,
3643207; 482966, 3643215; 482973,
3643223; 482975, 3643226; 482980,
3643231; 482984, 3643235; 482991,
3643242; 482995, 3643245; 482999,
3643248; 483002, 3643251; 483011,
3643257; 483019, 3643262; 483028,
3643267; 483037, 3643271; 483046,
3643274; 483056, 3643277; 483066,
3643280; 483075, 3643281; 483085,
3643282; 483091, 3643283; 483091,
3643283; 483101, 3643283; 483111,
3643283; 483121, 3643282; 483131,
3643280; 483138, 3643278; 483146,
3643277; 483149, 3643276; 483149,
3643276; 483151, 3643277; 483159,
3643282; 483168, 3643286; 483177,
3643291; 483179, 3643291; 483191,
3643296; 483198, 3643300; 483202,
3643301; 483211, 3643305; 483221,
3643308; 483231, 3643310; 483241,
3643311; 483245, 3643312; 483256,
3643313; 483261, 3643314; 483271,
3643314; 483273, 3643314; 483275,
3643314; 483275, 3643314; 483282,
3643314; 483289, 3643315; 483305,
3643315; 483308, 3643315; 483318,
3643315.
(ii) Subunit 2B. Land bounded by the
following UTM NAD27 coordinates
(E,N): 491618, 3644807; 491626,
3644807; 491658, 3644786; 491660,
3644784; 491662, 3644782; 491668,
3644775; 491675, 3644768; 491681,
3644760; 491687, 3644752; 491692,
3644744; 491697, 3644735; 491701,
3644726; 491702, 3644724; 491712,
3644699; 491715, 3644692; 491718,
3644682; 491718, 3644680; 491719,
PO 00000
Frm 00029
Fmt 4701
Sfmt 4702
11973
3644676; 491722, 3644667; 491724,
3644658; 491725, 3644657; 491726,
3644651; 491729, 3644642; 491730,
3644632; 491731, 3644622; 491731,
3644612; 491731, 3644602; 491730,
3644592; 491729, 3644582; 491728,
3644578; 491727, 3644575; 491726,
3644571; 491725, 3644566; 491724,
3644565; 491721, 3644555; 491719,
3644548; 491716, 3644541; 491713,
3644534; 491709, 3644524; 491705,
3644516; 491699, 3644507; 491694,
3644499; 491687, 3644491; 491687,
3644491; 491679, 3644482; 491672,
3644475; 491665, 3644468; 491657,
3644462; 491653, 3644459; 491647,
3644454; 491643, 3644451; 491634,
3644446; 491625, 3644441; 491623,
3644440; 491606, 3644432; 491600,
3644429; 491590, 3644426; 491587,
3644425; 491574, 3644421; 491568,
3644419; 491558, 3644417; 491550,
3644415; 491531, 3644412; 491529,
3644412; 491523, 3644412; 491502,
3644409; 491497, 3644409; 491496,
3644409; 491493, 3644409; 491487,
3644404; 491479, 3644399; 491475,
3644397; 491462, 3644390; 491457,
3644387; 491453, 3644386; 491444,
3644381; 491439, 3644379; 491429,
3644376; 491420, 3644373; 491410,
3644370; 491405, 3644370; 491399,
3644369; 491394, 3644368; 491384,
3644367; 491374, 3644366; 491372,
3644366; 491357, 3644367; 491348,
3644367; 491338, 3644368; 491331,
3644369; 491323, 3644371; 491321,
3644371; 491311, 3644373; 491301,
3644376; 491297, 3644378; 491287,
3644381; 491282, 3644383; 491273,
3644388; 491265, 3644391; 491260,
3644394; 491258, 3644395; 491250,
3644401; 491242, 3644406; 491234,
3644413; 491227, 3644420; 491225,
3644421; 491216, 3644431; 491214,
3644433; 491244, 3644474; 491289,
3644507; 491289, 3644561; 491293,
3644602; 491223, 3644651; 491174,
3644695; 491174, 3644697; 491174,
3644700; 491174, 3644703; 491175,
3644706; 491175, 3644709; 491176,
3644712; 491176, 3644714; 491177,
3644717; 491177, 3644720; 491178,
3644723; 491179, 3644726; 491180,
3644729; 491181, 3644731; 491181,
3644734; 491182, 3644737; 491183,
3644739; 491185, 3644742; 491186,
3644745; 491187, 3644747; 491188,
3644750; 491189, 3644753; 491191,
3644755; 491192, 3644758; 491194,
3644760; 491195, 3644763; 491197,
3644765; 491198, 3644768; 491200,
3644770; 491201, 3644773; 491203,
3644775; 491205, 3644777; 491207,
3644780; 491208, 3644782; 491210,
3644784; 491211, 3644785; 491220,
3644803; 491221, 3644805; 491226,
3644814; 491231, 3644823; 491237,
E:\FR\FM\14MRP2.SGM
14MRP2
cprice-sewell on PROD1PC66 with PROPOSALS2
11974
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
3644831; 491243, 3644838; 491250,
3644846; 491257, 3644853; 491265,
3644859; 491267, 3644861; 491274,
3644866; 491274, 3644866; 491283,
3644872; 491288, 3644876; 491296,
3644881; 491305, 3644886; 491314,
3644890; 491324, 3644893; 491333,
3644896; 491343, 3644899; 491352,
3644900; 491371, 3644894; 491449,
3644877; 491528, 3644849; 491618,
3644807.
(iii) Subunit 2C. Land bounded by the
following UTM NAD27 coordinates
(E,N): 501501, 3643932; 501493,
3643937; 501484, 3643943; 501483,
3643943; 501480, 3643945; 501474,
3643950; 501469, 3643953; 501467,
3643955; 501459, 3643961; 501450,
3643968; 501449, 3643969; 501448,
3643970; 501445, 3643972; 501437,
3643977; 501434, 3643979; 501433,
3643980; 501429, 3643981; 501428,
3643982; 501420, 3643986; 501417,
3643988; 501410, 3643992; 501404,
3643996; 501398, 3644000; 501393,
3644004; 501391, 3644006; 501387,
3644009; 501384, 3644011; 501376,
3644017; 501369, 3644023; 501366,
3644026; 501360, 3644031; 501355,
3644035; 501348, 3644043; 501347,
3644045; 501346, 3644045; 501344,
3644047; 501340, 3644051; 501339,
3644052; 501333, 3644059; 501329,
3644064; 501325, 3644068; 501323,
3644071; 501317, 3644079; 501312,
3644088; 501307, 3644097; 501305,
3644101; 501300, 3644108; 501297,
3644114; 501292, 3644123; 501288,
3644132; 501284, 3644141; 501281,
3644151; 501279, 3644161; 501277,
3644171; 501277, 3644174; 501275,
3644190; 501275, 3644196; 501274,
3644206; 501275, 3644216; 501276,
3644226; 501277, 3644236; 501279,
3644245; 501280, 3644247; 501280,
3644248; 501282, 3644254; 501284,
3644262; 501286, 3644266; 501289,
3644275; 501293, 3644284; 501298,
3644293; 501300, 3644297; 501305,
3644305; 501308, 3644309; 501314,
3644317; 501320, 3644325; 501327,
3644332; 501334, 3644339; 501342,
3644346; 501350, 3644351; 501352,
3644352; 501359, 3644357; 501366,
3644361; 501375, 3644366; 501384,
3644370; 501385, 3644371; 501398,
3644376; 501407, 3644379; 501416,
3644382; 501426, 3644384; 501436,
3644386; 501437, 3644386; 501461,
3644389; 501470, 3644390; 501480,
3644390; 501490, 3644390; 501499,
3644389; 501509, 3644387; 501516,
3644386; 501543, 3644379; 501555,
3644378; 501556, 3644378; 501566,
3644377; 501567, 3644377; 501572,
3644376; 501578, 3644376; 501580,
3644376; 501587, 3644377; 501591,
3644378; 501625, 3644382; 501625,
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
3644382; 501635, 3644383; 501641,
3644383; 501657, 3644384; 501710,
3644389; 501711, 3644389; 501728,
3644391; 501755, 3644399; 501759,
3644400; 501769, 3644402; 501771,
3644403; 501793, 3644407; 501801,
3644408; 501811, 3644409; 501821,
3644409; 501831, 3644409; 501841,
3644408; 501841, 3644408; 501869,
3644404; 501882, 3644402; 501883,
3644402; 501887, 3644402; 501888,
3644401; 501894, 3644401; 501904,
3644401; 501908, 3644401; 501930,
3644399; 501933, 3644399; 501979,
3644393; 501982, 3644393; 501990,
3644392; 502033, 3644384; 502067,
3644378; 502083, 3644376; 502134,
3644369; 502156, 3644367; 502165,
3644367; 502165, 3644367; 502197,
3644362; 502228, 3644359; 502231,
3644358; 502240, 3644357; 502242,
3644356; 502270, 3644351; 502278,
3644349; 502287, 3644346; 502296,
3644342; 502306, 3644338; 502314,
3644333; 502321, 3644329; 502339,
3644318; 502371, 3644300; 502406,
3644281; 502425, 3644272; 502429,
3644270; 502433, 3644268; 502479,
3644243; 502484, 3644241; 502492,
3644236; 502498, 3644232; 502521,
3644215; 502524, 3644213; 502524,
3644213; 502551, 3644192; 502559,
3644186; 502566, 3644179; 502573,
3644172; 502577, 3644166; 502590,
3644150; 502592, 3644148; 502598,
3644140; 502603, 3644131; 502605,
3644127; 502615, 3644108; 502617,
3644104; 502618, 3644103; 502621,
3644097; 502624, 3644091; 502626,
3644089; 502630, 3644080; 502631,
3644079; 502633, 3644074; 502639,
3644065; 502653, 3644043; 502657,
3644036; 502660, 3644032; 502673,
3644006; 502676, 3644001; 502680,
3643992; 502681, 3643989; 502702,
3643936; 502704, 3643930; 502706,
3643921; 502707, 3643920; 502713,
3643896; 502728, 3643863; 502736,
3643845; 502738, 3643842; 502745,
3643827; 502747, 3643822; 502750,
3643813; 502751, 3643812; 502752,
3643809; 502752, 3643809; 502755,
3643805; 502764, 3643787; 502773,
3643775; 502783, 3643765; 502786,
3643762; 502787, 3643761; 502802,
3643746; 502819, 3643731; 502819,
3643730; 502842, 3643710; 502843,
3643709; 502847, 3643705; 502854,
3643701; 502856, 3643699; 502870,
3643689; 502873, 3643687; 502892,
3643673; 502901, 3643667; 502902,
3643666; 502907, 3643664; 502907,
3643663; 502910, 3643663; 502914,
3643662; 502915, 3643662; 502920,
3643661; 502925, 3643660; 502928,
3643660; 502958, 3643655; 502973,
3643654; 502996, 3643652; 503014,
3643651; 503033, 3643650; 503063,
PO 00000
Frm 00030
Fmt 4701
Sfmt 4702
3643650; 503070, 3643649; 503080,
3643648; 503089, 3643647; 503099,
3643644; 503103, 3643643; 503170,
3643623; 503176, 3643622; 503179,
3643620; 503196, 3643614; 503202,
3643612; 503208, 3643609; 503231,
3643599; 503234, 3643597; 503242,
3643592; 503249, 3643589; 503269,
3643576; 503271, 3643574; 503279,
3643569; 503284, 3643564; 503306,
3643546; 503309, 3643544; 503313,
3643539; 503331, 3643522; 503334,
3643520; 503339, 3643514; 503352,
3643500; 503354, 3643498; 503360,
3643491; 503372, 3643474; 503373,
3643474; 503378, 3643466; 503384,
3643457; 503388, 3643450; 503397,
3643431; 503398, 3643430; 503402,
3643421; 503406, 3643411; 503409,
3643402; 503409, 3643400; 503413,
3643384; 503415, 3643376; 503416,
3643366; 503417, 3643356; 503418,
3643346; 503418, 3643342; 503418,
3643342; 503417, 3643332; 503417,
3643328; 503416, 3643313; 503415,
3643307; 503414, 3643299; 503411,
3643283; 503410, 3643281; 503408,
3643272; 503405, 3643257; 503404,
3643256; 503401, 3643247; 503398,
3643237; 503395, 3643230; 503391,
3643222; 503390, 3643220; 503385,
3643212; 503380, 3643203; 503377,
3643198; 503376, 3643198; 503371,
3643189; 503364, 3643182; 503357,
3643174; 503356, 3643173; 503350,
3643167; 503343, 3643161; 503336,
3643155; 503328, 3643149; 503323,
3643146; 503307, 3643136; 503303,
3643133; 503294, 3643129; 503285,
3643124; 503275, 3643121; 503270,
3643119; 503251, 3643114; 503247,
3643113; 503238, 3643110; 503231,
3643109; 503216, 3643107; 503213,
3643106; 503203, 3643105; 503193,
3643105; 503183, 3643105; 503173,
3643106; 503168, 3643107; 503145,
3643111; 503144, 3643111; 503133,
3643113; 503129, 3643114; 503119,
3643116; 503110, 3643119; 503103,
3643121; 503093, 3643125; 503087,
3643127; 503078, 3643130; 503069,
3643133; 503060, 3643137; 503052,
3643141; 503037, 3643146; 503032,
3643148; 503023, 3643153; 503015,
3643157; 502997, 3643167; 502997,
3643167; 502988, 3643173; 502980,
3643178; 502979, 3643180; 502962,
3643192; 502946, 3643203; 502944,
3643204; 502936, 3643210; 502927,
3643215; 502921, 3643219; 502913,
3643225; 502911, 3643226; 502902,
3643233; 502885, 3643245; 502877,
3643250; 502870, 3643257; 502867,
3643259; 502856, 3643265; 502852,
3643267; 502846, 3643271; 502830,
3643272; 502817, 3643271; 502800,
3643270; 502781, 3643268; 502769,
3643266; 502753, 3643263; 502747,
E:\FR\FM\14MRP2.SGM
14MRP2
cprice-sewell on PROD1PC66 with PROPOSALS2
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
3643262; 502737, 3643261; 502727,
3643261; 502707, 3643261; 502707,
3643261; 502697, 3643261; 502687,
3643262; 502686, 3643262; 502677,
3643263; 502667, 3643265; 502657,
3643267; 502648, 3643270; 502638,
3643274; 502632, 3643276; 502619,
3643283; 502616, 3643284; 502607,
3643289; 502599, 3643294; 502596,
3643296; 502596, 3643296; 502592,
3643298; 502590, 3643298; 502581,
3643302; 502568, 3643309; 502567,
3643309; 502558, 3643314; 502558,
3643314; 502557, 3643315; 502557,
3643315; 502543, 3643321; 502536,
3643324; 502536, 3643324; 502527,
3643328; 502522, 3643330; 502511,
3643337; 502507, 3643339; 502498,
3643344; 502482, 3643353; 502480,
3643354; 502477, 3643355; 502456,
3643368; 502450, 3643372; 502442,
3643378; 502438, 3643381; 502425,
3643392; 502422, 3643394; 502415,
3643401; 502414, 3643402; 502405,
3643412; 502399, 3643418; 502392,
3643426; 502391, 3643427; 502383,
3643438; 502374, 3643450; 502373,
3643451; 502372, 3643452; 502363,
3643465; 502358, 3643472; 502352,
3643480; 502352, 3643481; 502330,
3643518; 502326, 3643527; 502322,
3643536; 502318, 3643545; 502317,
3643548; 502311, 3643566; 502306,
3643578; 502303, 3643584; 502300,
3643591; 502294, 3643610; 502293,
3643612; 502292, 3643615; 502284,
3643640; 502282, 3643646; 502280,
3643656; 502280, 3643659; 502277,
3643676; 502276, 3643682; 502275,
3643692; 502274, 3643701; 502274,
3643701; 502274, 3643711; 502274,
3643721; 502275, 3643728; 502276,
3643740; 502276, 3643742; 502278,
3643758; 502278, 3643759; 502279,
3643763; 502282, 3643779; 502282,
3643780; 502284, 3643791; 502284,
3643795; 502286, 3643801; 502287,
3643805; 502289, 3643818; 502291,
3643828; 502291, 3643833; 502291,
3643837; 502290, 3643846; 502290,
3643847; 502290, 3643847; 502287,
3643855; 502286, 3643857; 502285,
3643859; 502282, 3643864; 502278,
3643868; 502277, 3643869; 502259,
3643874; 502254, 3643876; 502245,
3643879; 502237, 3643883; 502229,
3643887; 502225, 3643888; 502211,
3643892; 502209, 3643893; 502194,
3643898; 502187, 3643900; 502185,
3643900; 502182, 3643901; 502179,
3643902; 502170, 3643903; 502162,
3643904; 502156, 3643905; 502144,
3643906; 502120, 3643906; 502114,
3643907; 502111, 3643907; 502095,
3643908; 502093, 3643908; 502056,
3643912; 502052, 3643913; 502042,
3643914; 502032, 3643917; 502029,
3643918; 502016, 3643921; 502010,
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
3643923; 502009, 3643924; 501989,
3643931; 501981, 3643933; 501971,
3643936; 501969, 3643932; 501969,
3643930; 501966, 3643924; 501964,
3643916; 501962, 3643911; 501961,
3643900; 501960, 3643893; 501959,
3643889; 501959, 3643879; 501959,
3643876; 501959, 3643874; 501957,
3643860; 501957, 3643846; 501957,
3643845; 501956, 3643841; 501957,
3643827; 501957, 3643820; 501957,
3643810; 501956, 3643800; 501955,
3643793; 501953, 3643784; 501953,
3643777; 501952, 3643774; 501951,
3643765; 501950, 3643761; 501947,
3643747; 501945, 3643741; 501942,
3643731; 501941, 3643726; 501934,
3643708; 501932, 3643704; 501928,
3643695; 501923, 3643686; 501918,
3643677; 501912, 3643669; 501906,
3643661; 501899, 3643654; 501892,
3643647; 501884, 3643641; 501876,
3643635; 501873, 3643634; 501865,
3643628; 501859, 3643624; 501850,
3643620; 501842, 3643616; 501828,
3643610; 501827, 3643610; 501817,
3643606; 501808, 3643603; 501803,
3643602; 501790, 3643599; 501785,
3643598; 501785, 3643598; 501775,
3643596; 501765, 3643595; 501755,
3643595; 501745, 3643595; 501736,
3643596; 501726, 3643598; 501723,
3643599; 501713, 3643601; 501707,
3643602; 501697, 3643605; 501688,
3643609; 501679, 3643613; 501670,
3643617; 501664, 3643621; 501648,
3643631; 501645, 3643633; 501637,
3643639; 501629, 3643645; 501623,
3643651; 501618, 3643656; 501617,
3643657; 501612, 3643662; 501611,
3643664; 501607, 3643667; 501602,
3643673; 501590, 3643686; 501588,
3643688; 501582, 3643696; 501576,
3643704; 501571, 3643712; 501566,
3643721; 501562, 3643730; 501561,
3643733; 501558, 3643739; 501557,
3643743; 501552, 3643756; 501551,
3643759; 501548, 3643768; 501546,
3643778; 501546, 3643779; 501545,
3643785; 501544, 3643791; 501542,
3643799; 501542, 3643802; 501541,
3643812; 501541, 3643822; 501541,
3643828; 501542, 3643845; 501542,
3643849; 501543, 3643857; 501544,
3643873; 501545, 3643874; 501546,
3643881; 501548, 3643895; 501549,
3643898; 501551, 3643908; 501552,
3643909; 501551, 3643909; 501548,
3643911; 501540, 3643913; 501529,
3643918; 501527, 3643918; 501518,
3643923; 501515, 3643924; 501507,
3643929; 501501, 3643932.
(iv) Subunit 2D. Land bounded by the
following UTM NAD27 coordinates
(E,N): 504291, 3640664; 504292,
3640667; 504360, 3640637; 504432,
3640633; 504488, 3640633; 504526,
3640599; 504586, 3640595; 504647,
PO 00000
Frm 00031
Fmt 4701
Sfmt 4702
11975
3640580; 504711, 3640535; 504745,
3640542; 504821, 3640565; 504866,
3640542; 504987, 3640546; 505135,
3640580; 505138, 3640574; 505142,
3640566; 505148, 3640550; 505149,
3640550; 505152, 3640540; 505155,
3640531; 505157, 3640521; 505157,
3640521; 505161, 3640516; 505166,
3640508; 505170, 3640499; 505176,
3640487; 505177, 3640487; 505181,
3640478; 505184, 3640468; 505187,
3640459; 505189, 3640449; 505191,
3640439; 505192, 3640429; 505192,
3640419; 505192, 3640419; 505192,
3640406; 505192, 3640396; 505191,
3640386; 505189, 3640376; 505187,
3640366; 505185, 3640357; 505181,
3640346; 505181, 3640346; 505177,
3640336; 505173, 3640327; 505168,
3640319; 505163, 3640310; 505157,
3640302; 505151, 3640294; 505144,
3640287; 505137, 3640280; 505129,
3640274; 505121, 3640268; 505112,
3640263; 505104, 3640258; 505090,
3640251; 505089, 3640251; 505080,
3640247; 505071, 3640243; 505061,
3640240; 505051, 3640238; 505042,
3640236; 505032, 3640235; 505031,
3640235; 505012, 3640234; 505003,
3640234; 504993, 3640234; 504983,
3640235; 504973, 3640237; 504967,
3640238; 504962, 3640237; 504958,
3640236; 504948, 3640235; 504938,
3640234; 504928, 3640233; 504918,
3640234; 504908, 3640235; 504898,
3640236; 504898, 3640236; 504886,
3640239; 504876, 3640241; 504867,
3640244; 504857, 3640247; 504848,
3640251; 504839, 3640256; 504831,
3640261; 504823, 3640267; 504815,
3640274; 504808, 3640280; 504801,
3640288; 504795, 3640295; 504789,
3640303; 504786, 3640309; 504782,
3640304; 504778, 3640301; 504771,
3640294; 504763, 3640288; 504755,
3640282; 504752, 3640279; 504724,
3640262; 504719, 3640259; 504710,
3640254; 504701, 3640250; 504691,
3640246; 504689, 3640246; 504670,
3640240; 504663, 3640237; 504653,
3640235; 504643, 3640234; 504633,
3640233; 504623, 3640232; 504614,
3640233; 504594, 3640234; 504593,
3640234; 504583, 3640235; 504573,
3640236; 504563, 3640239; 504556,
3640241; 504554, 3640242; 504535,
3640243; 504527, 3640244; 504518,
3640246; 504508, 3640248; 504498,
3640251; 504489, 3640254; 504480,
3640258; 504471, 3640263; 504463,
3640268; 504454, 3640274; 504454,
3640274; 504454, 3640274; 504432,
3640268; 504430, 3640268; 504421,
3640265; 504411, 3640264; 504401,
3640263; 504391, 3640262; 504381,
3640263; 504371, 3640264; 504361,
3640265; 504351, 3640268; 504342,
3640270; 504333, 3640274; 504332,
E:\FR\FM\14MRP2.SGM
14MRP2
11976
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
cprice-sewell on PROD1PC66 with PROPOSALS2
3640274; 504315, 3640281; 504306,
3640285; 504297, 3640290; 504289,
3640295; 504280, 3640301; 504273,
3640307; 504265, 3640314; 504259,
3640322; 504252, 3640329; 504246,
3640337; 504241, 3640346; 504237,
3640353; 504216, 3640396; 504215,
3640397; 504211, 3640406; 504208,
3640415; 504205, 3640425; 504203,
3640433; 504200, 3640445; 504200,
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
3640446; 504198, 3640456; 504197,
3640466; 504197, 3640476; 504197,
3640486; 504198, 3640496; 504199,
3640498; 504201, 3640515; 504202,
3640523; 504205, 3640532; 504208,
3640542; 504211, 3640551; 504215,
3640560; 504220, 3640569; 504225,
3640578; 504231, 3640586; 504237,
3640593; 504244, 3640601; 504248,
3640604; 504258, 3640614; 504262,
PO 00000
Frm 00032
Fmt 4701
Sfmt 4702
3640617; 504270, 3640624; 504278,
3640629; 504286, 3640635; 504286,
3640635; 504287, 3640644; 504287,
3640644; 504289, 3640654; 504291,
3640664.
(v) Note: Map of Unit 2, subunits 2A,
2B, 2C, and 2D (Map 3), follows:
BILLING CODE 4310–55–P
E:\FR\FM\14MRP2.SGM
14MRP2
11977
BILLING CODE 4310–55–C
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
PO 00000
Frm 00033
Fmt 4701
Sfmt 4702
E:\FR\FM\14MRP2.SGM
14MRP2
EP14MR07.002
cprice-sewell on PROD1PC66 with PROPOSALS2
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
cprice-sewell on PROD1PC66 with PROPOSALS2
11978
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
(8) Unit 3: San Diego County,
California. From USGS 1:24,000
quadrangle maps Alpine and Viejas
Mountain.
(i) Subunit 3A. Land bounded by the
following UTM NAD27 coordinates
(E,N): 523323, 3635057; 523320,
3635057; 523317, 3635056; 523314,
3635056; 523311, 3635056; 523308,
3635055; 523305, 3635055; 523303,
3635055; 523300, 3635055; 523297,
3635055; 523294, 3635055; 523291,
3635055; 523288, 3635055; 523285,
3635055; 523282, 3635056; 523279,
3635056; 523276, 3635056; 523274,
3635057; 523271, 3635057; 523266,
3635056; 523256, 3635054; 523255,
3635054; 523217, 3635049; 523208,
3635049; 523198, 3635048; 523188,
3635049; 523178, 3635050; 523169,
3635051; 523159, 3635053; 523149,
3635056; 523143, 3635059; 523141,
3635059; 523138, 3635060; 523136,
3635061; 523133, 3635062; 523130,
3635062; 523127, 3635063; 523125,
3635064; 523122, 3635065; 523119,
3635067; 523116, 3635068; 523114,
3635069; 523111, 3635070; 523109,
3635071; 523106, 3635073; 523104,
3635074; 523101, 3635076; 523099,
3635077; 523096, 3635079; 523094,
3635080; 523091, 3635082; 523089,
3635084; 523087, 3635085; 523084,
3635087; 523082, 3635089; 523080,
3635091; 523078, 3635093; 523075,
3635095; 523073, 3635097; 523071,
3635099; 523069, 3635101; 523067,
3635103; 523065, 3635105; 523063,
3635107; 523061, 3635109; 523060,
3635112; 523058, 3635114; 523056,
3635116; 523054, 3635119; 523053,
3635121; 523051, 3635123; 523049,
3635126; 523048, 3635128; 523046,
3635131; 523045, 3635133; 523044,
3635136; 523042, 3635138; 523041,
3635141; 523040, 3635144; 523039,
3635146; 523038, 3635148; 523037,
3635149; 523033, 3635158; 523028,
3635167; 523025, 3635176; 523022,
3635186; 523020, 3635196; 523018,
3635205; 523017, 3635212; 523016,
3635231; 523015, 3635234; 523015,
3635244; 523015, 3635254; 523016,
3635264; 523018, 3635274; 523020,
3635284; 523023, 3635293; 523026,
3635302; 523032, 3635317; 523033,
3635318; 523037, 3635327; 523042,
3635336; 523047, 3635344; 523053,
3635352; 523059, 3635360; 523066,
3635367; 523073, 3635374; 523081,
3635380; 523086, 3635384; 523103,
3635396; 523106, 3635398; 523115,
3635404; 523123, 3635408; 523133,
3635412; 523142, 3635416; 523151,
3635419; 523161, 3635421; 523169,
3635422; 523218, 3635430; 523220,
3635430; 523230, 3635431; 523240,
3635431; 523250, 3635431; 523260,
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
3635430; 523267, 3635429; 523281,
3635426; 523283, 3635426; 523293,
3635423; 523303, 3635421; 523312,
3635417; 523321, 3635413; 523330,
3635408; 523338, 3635403; 523347,
3635397; 523354, 3635391; 523362,
3635384; 523368, 3635377; 523375,
3635369; 523380, 3635361; 523389,
3635348; 523390, 3635347; 523395,
3635339; 523400, 3635330; 523404,
3635321; 523407, 3635313; 523408,
3635312; 523410, 3635309; 523412,
3635307; 523414, 3635305; 523416,
3635303; 523417, 3635300; 523419,
3635298; 523421, 3635296; 523423,
3635293; 523424, 3635291; 523426,
3635289; 523427, 3635286; 523429,
3635284; 523430, 3635281; 523432,
3635278; 523433, 3635276; 523434,
3635273; 523435, 3635271; 523437,
3635268; 523438, 3635265; 523439,
3635263; 523440, 3635260; 523441,
3635257; 523442, 3635254; 523443,
3635252; 523443, 3635249; 523444,
3635246; 523445, 3635243; 523446,
3635240; 523446, 3635238; 523447,
3635235; 523447, 3635232; 523448,
3635229; 523448, 3635226; 523448,
3635223; 523449, 3635220; 523449,
3635217; 523449, 3635215; 523449,
3635212; 523449, 3635209; 523449,
3635206; 523449, 3635203; 523449,
3635200; 523449, 3635197; 523449,
3635194; 523448, 3635191; 523448,
3635189; 523448, 3635186; 523447,
3635183; 523447, 3635180; 523446,
3635177; 523446, 3635174; 523445,
3635171; 523444, 3635169; 523443,
3635166; 523443, 3635163; 523442,
3635160; 523441, 3635157; 523440,
3635155; 523439, 3635152; 523438,
3635149; 523437, 3635147; 523435,
3635144; 523434, 3635141; 523433,
3635139; 523432, 3635136; 523430,
3635134; 523429, 3635131; 523427,
3635129; 523426, 3635126; 523424,
3635124; 523423, 3635121; 523421,
3635119; 523419, 3635117; 523417,
3635114; 523416, 3635112; 523414,
3635110; 523412, 3635107; 523410,
3635105; 523408, 3635103; 523406,
3635101; 523404, 3635099; 523402,
3635097; 523400, 3635095; 523398,
3635093; 523395, 3635091; 523393,
3635089; 523391, 3635087; 523389,
3635086; 523386, 3635084; 523384,
3635082; 523382, 3635081; 523379,
3635079; 523377, 3635077; 523374,
3635076; 523372, 3635075; 523369,
3635073; 523367, 3635072; 523364,
3635070; 523361, 3635069; 523359,
3635068; 523356, 3635067; 523353,
3635066; 523351, 3635065; 523348,
3635064; 523345, 3635063; 523342,
3635062; 523340, 3635061; 523337,
3635060; 523334, 3635059; 523331,
3635059; 523328, 3635058; 523326,
3635058; 523323, 3635057.
PO 00000
Frm 00034
Fmt 4701
Sfmt 4702
(ii) Subunit 3B. Land bounded by the
following UTM NAD27 coordinates
(E,N): 524731, 3634052; 524721,
3634052; 524711, 3634052; 524701,
3634053; 524701, 3634053; 524621,
3634064; 524612, 3634066; 524602,
3634068; 524593, 3634070; 524547,
3634086; 524546, 3634086; 524536,
3634090; 524527, 3634094; 524519,
3634099; 524510, 3634104; 524502,
3634110; 524494, 3634116; 524487,
3634123; 524480, 3634130; 524474,
3634138; 524468, 3634146; 524463,
3634154; 524450, 3634177; 524450,
3634177; 524445, 3634186; 524441,
3634195; 524437, 3634204; 524434,
3634214; 524432, 3634223; 524430,
3634233; 524429, 3634243; 524429,
3634249; 524428, 3634293; 524428,
3634298; 524428, 3634308; 524429,
3634317; 524431, 3634327; 524433,
3634337; 524436, 3634347; 524439,
3634356; 524444, 3634365; 524448,
3634374; 524452, 3634380; 524469,
3634407; 524471, 3634409; 524477,
3634418; 524483, 3634425; 524490,
3634433; 524497, 3634439; 524505,
3634446; 524513, 3634452; 524522,
3634457; 524530, 3634461; 524539,
3634466; 524549, 3634469; 524557,
3634472; 524601, 3634484; 524603,
3634484; 524607, 3634485; 524617,
3634500; 524621, 3634504; 524627,
3634512; 524634, 3634519; 524641,
3634526; 524647, 3634531; 524683,
3634560; 524686, 3634562; 524694,
3634568; 524702, 3634573; 524711,
3634578; 524720, 3634582; 524729,
3634585; 524739, 3634588; 524749,
3634590; 524758, 3634592; 524768,
3634593; 524778, 3634593; 524783,
3634593; 524811, 3634592; 524816,
3634592; 524826, 3634591; 524836,
3634590; 524845, 3634587; 524855,
3634584; 524864, 3634581; 524873,
3634577; 524882, 3634572; 524891,
3634567; 524899, 3634561; 524907,
3634555; 524914, 3634548; 524917,
3634544; 524933, 3634527; 524937,
3634523; 524943, 3634516; 524949,
3634508; 524954, 3634499; 524959,
3634490; 524963, 3634481; 524966,
3634472; 524986, 3634414; 524987,
3634413; 524990, 3634403; 524992,
3634394; 524993, 3634384; 524994,
3634374; 524995, 3634364; 524994,
3634354; 524993, 3634344; 524992,
3634334; 524990, 3634325; 524987,
3634315; 524985, 3634311; 524970,
3634270; 524968, 3634265; 524964,
3634255; 524959, 3634247; 524957,
3634243; 524957, 3634242; 524953,
3634220; 524952, 3634214; 524950,
3634204; 524947, 3634194; 524943,
3634185; 524939, 3634176; 524935,
3634167; 524929, 3634159; 524923,
3634150; 524917, 3634143; 524913,
3634139; 524890, 3634114; 524887,
E:\FR\FM\14MRP2.SGM
14MRP2
cprice-sewell on PROD1PC66 with PROPOSALS2
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
3634111; 524880, 3634104; 524872,
3634098; 524864, 3634092; 524856,
3634087; 524847, 3634082; 524838,
3634078; 524832, 3634076; 524804,
3634066; 524801, 3634065; 524791,
3634062; 524781, 3634059; 524774,
3634058; 524744, 3634054; 524741,
3634053; 524731, 3634052. Land
bounded by 524035, 3634354; 524039,
3634359; 524047, 3634357; 524095,
3634347; 524126, 3634351; 524148,
3634359; 524156, 3634391; 524158,
3634419; 524172, 3634438; 524173,
3634455; 524177, 3634456; 524184,
3634459; 524193, 3634462; 524203,
3634464; 524213, 3634465; 524223,
3634466; 524233, 3634467; 524243,
3634466; 524252, 3634465; 524262,
3634464; 524272, 3634462; 524282,
3634459; 524291, 3634455; 524300,
3634451; 524309, 3634446; 524315,
3634442; 524342, 3634425; 524344,
3634424; 524352, 3634418; 524360,
3634411; 524367, 3634405; 524374,
3634397; 524381, 3634390; 524386,
3634381; 524389, 3634377; 524400,
3634360; 524402, 3634356; 524407,
3634347; 524411, 3634338; 524415,
3634329; 524417, 3634319; 524420,
3634310; 524421, 3634300; 524422,
3634290; 524423, 3634280; 524423,
3634275; 524422, 3634242; 524421,
3634237; 524420, 3634227; 524419,
3634217; 524416, 3634207; 524413,
3634198; 524411, 3634190; 524399,
3634160; 524398, 3634158; 524394,
3634149; 524389, 3634140; 524384,
3634132; 524378, 3634124; 524372,
3634116; 524367, 3634110; 524384,
3634112; 524388, 3634112; 524398,
3634112; 524408, 3634112; 524418,
3634111; 524428, 3634109; 524438,
3634107; 524447, 3634104; 524457,
3634101; 524466, 3634097; 524474,
3634092; 524483, 3634087; 524491,
3634081; 524499, 3634074; 524506,
3634068; 524513, 3634060; 524519,
3634053; 524519, 3634052; 524543,
3634021; 524549, 3634013; 524554,
3634005; 524559, 3633996; 524563,
3633987; 524566, 3633978; 524569,
3633968; 524572, 3633958; 524573,
3633948; 524574, 3633938; 524575,
3633933; 524576, 3633885; 524576,
3633881; 524575, 3633871; 524575,
3633861; 524573, 3633852; 524571,
3633842; 524568, 3633832; 524565,
3633825; 524563, 3633821; 524571,
3633826; 524579, 3633831; 524588,
3633836; 524597, 3633840; 524606,
3633844; 524613, 3633846; 524683,
3633866; 524686, 3633867; 524695,
3633869; 524705, 3633870; 524715,
3633871; 524725, 3633872; 524735,
3633871; 524745, 3633870; 524755,
3633869; 524764, 3633867; 524774,
3633864; 524783, 3633860; 524792,
3633856; 524801, 3633851; 524810,
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
3633846; 524818, 3633840; 524826,
3633834; 524833, 3633827; 524840,
3633820; 524846, 3633812; 524852,
3633804; 524857, 3633796; 524862,
3633787; 524866, 3633778; 524869,
3633768; 524871, 3633763; 524896,
3633679; 524897, 3633675; 524900,
3633665; 524901, 3633655; 524902,
3633645; 524902, 3633635; 524902,
3633625; 524901, 3633615; 524900,
3633606; 524897, 3633596; 524894,
3633586; 524891, 3633577; 524887,
3633568; 524882, 3633559; 524877,
3633551; 524871, 3633542; 524865,
3633535; 524858, 3633527; 524851,
3633521; 524844, 3633515; 524805,
3633485; 524768, 3633441; 524700,
3633357; 524665, 3633291; 524604,
3633162; 524603, 3633158; 524598,
3633150; 524593, 3633141; 524590,
3633137; 524449, 3633137; 524449,
3633180; 524437, 3633224; 524431,
3633250; 524419, 3633283; 524395,
3633287; 524381, 3633260; 524371,
3633220; 524366, 3633180; 524356,
3633155; 524345, 3633133; 524345,
3633133; 524339, 3633141; 524338,
3633144; 524280, 3633234; 524276,
3633240; 524271, 3633249; 524267,
3633258; 524264, 3633267; 524261,
3633277; 524259, 3633287; 524257,
3633297; 524256, 3633306; 524256,
3633316; 524256, 3633326; 524257,
3633336; 524259, 3633346; 524261,
3633356; 524264, 3633365; 524267,
3633375; 524271, 3633384; 524276,
3633393; 524281, 3633401; 524287,
3633409; 524291, 3633414; 524317,
3633446; 524318, 3633447; 524322,
3633483; 524322, 3633484; 524324,
3633494; 524326, 3633503; 524329,
3633513; 524333, 3633522; 524337,
3633531; 524342, 3633540; 524347,
3633549; 524353, 3633557; 524353,
3633557; 524462, 3633699; 524456,
3633695; 524448, 3633691; 524438,
3633686; 524429, 3633683; 524420,
3633680; 524410, 3633678; 524400,
3633676; 524390, 3633675; 524383,
3633675; 524328, 3633674; 524325,
3633674; 524315, 3633674; 524305,
3633675; 524295, 3633677; 524285,
3633679; 524276, 3633682; 524266,
3633685; 524265, 3633686; 524230,
3633701; 524222, 3633705; 524213,
3633709; 524205, 3633714; 524197,
3633720; 524189, 3633727; 524182,
3633733; 524175, 3633741; 524168,
3633748; 524163, 3633757; 524157,
3633765; 524153, 3633774; 524148,
3633783; 524145, 3633792; 524142,
3633802; 524140, 3633812; 524139,
3633815; 524127, 3633882; 524126,
3633888; 524125, 3633898; 524125,
3633908; 524125, 3633918; 524126,
3633928; 524127, 3633933; 524123,
3633932; 524113, 3633933; 524103,
3633934; 524093, 3633935; 524083,
PO 00000
Frm 00035
Fmt 4701
Sfmt 4702
11979
3633938; 524074, 3633941; 524065,
3633944; 524043, 3633953; 524043,
3633953; 524034, 3633957; 524025,
3633962; 524016, 3633967; 524008,
3633973; 524001, 3633979; 523993,
3633986; 523986, 3633993; 523980,
3634001; 523974, 3634009; 523969,
3634018; 523964, 3634027; 523960,
3634036; 523957, 3634045; 523954,
3634054; 523954, 3634055; 523946,
3634083; 523944, 3634092; 523943,
3634102; 523942, 3634112; 523941,
3634122; 523942, 3634132; 523943,
3634142; 523944, 3634148; 523954,
3634206; 523954, 3634210; 523957,
3634219; 523959, 3634229; 523963,
3634238; 523967, 3634247; 523972,
3634256; 523976, 3634262; 524028,
3634344; 524029, 3634346; 524035,
3634354.
(iii) Subunit 3C. Land bounded by the
following UTM NAD27 coordinates
(E,N): 527113, 3634393; 527120,
3634389; 527111, 3634389; 527111,
3634111; 527113, 3633915; 527118,
3633794; 527114, 3633788; 527113,
3633774; 527112, 3633774; 527093,
3633707; 527076, 3633649; 527039,
3633580; 527011, 3633527; 526971,
3633497; 526913, 3633452; 526859,
3633439; 526776, 3633426; 526708,
3633424; 526665, 3633413; 526631,
3633392; 526626, 3633391; 526620,
3633369; 526618, 3633363; 526614,
3633353; 526610, 3633344; 526606,
3633335; 526601, 3633328; 526570,
3633281; 526556, 3633238; 526555,
3633238; 526552, 3633229; 526548,
3633220; 526543, 3633211; 526541,
3633208; 526515, 3633165; 526512,
3633159; 526506, 3633151; 526499,
3633143; 526493, 3633136; 526485,
3633129; 526478, 3633123; 526470,
3633117; 526461, 3633112; 526452,
3633107; 526443, 3633103; 526434,
3633099; 526424, 3633096; 526415,
3633094; 526405, 3633093; 526402,
3633092; 526376, 3633089; 526369,
3633089; 526359, 3633088; 526349,
3633089; 526339, 3633090; 526329,
3633091; 526319, 3633093; 526310,
3633096; 526300, 3633100; 526291,
3633104; 526282, 3633109; 526274,
3633114; 526266, 3633120; 526258,
3633126; 526251, 3633133; 526244,
3633140; 526238, 3633148; 526221,
3633170; 526221, 3633170; 526215,
3633178; 526209, 3633187; 526205,
3633195; 526201, 3633205; 526197,
3633214; 526194, 3633223; 526194,
3633225; 526175, 3633297; 526173,
3633306; 526171, 3633315; 526171,
3633325; 526170, 3633335; 526170,
3633340; 526173, 3633452; 526174,
3633458; 526175, 3633468; 526176,
3633478; 526179, 3633487; 526181,
3633497; 526185, 3633506; 526189,
3633515; 526194, 3633524; 526199,
E:\FR\FM\14MRP2.SGM
14MRP2
cprice-sewell on PROD1PC66 with PROPOSALS2
11980
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
3633532; 526192, 3633537; 526183,
3633543; 526176, 3633549; 526169,
3633555; 526138, 3633586; 526137,
3633587; 526131, 3633594; 526124,
3633602; 526118, 3633610; 526113,
3633618; 526109, 3633627; 526104,
3633636; 526101, 3633646; 526098,
3633655; 526096, 3633665; 526094,
3633675; 526093, 3633684; 526090,
3633734; 526085, 3633793; 526074,
3633870; 526074, 3633871; 526064,
3633943; 526064, 3633944; 526063,
3633954; 526062, 3633964; 526063,
3633974; 526064, 3633984; 526064,
3633986; 526073, 3634048; 526074,
3634056; 526076, 3634066; 526079,
3634076; 526083, 3634085; 526084,
3634088; 526100, 3634123; 526100,
3634133; 526091, 3634181; 526070,
3634267; 526069, 3634273; 526068,
3634278; 526058, 3634337; 526058,
3634342; 526057, 3634352; 526057,
3634353; 526054, 3634397; 526054,
3634406; 526054, 3634416; 526055,
3634426; 526057, 3634435; 526059,
3634445; 526062, 3634455; 526066,
3634464; 526070, 3634473; 526074,
3634482; 526080, 3634490; 526085,
3634498; 526092, 3634506; 526099,
3634513; 526102, 3634517; 526123,
3634536; 526127, 3634540; 526134,
3634546; 526143, 3634552; 526151,
3634557; 526160, 3634562; 526169,
3634566; 526178, 3634570; 526187,
3634572; 526213, 3634579; 526214,
3634580; 526224, 3634582; 526234,
3634584; 526235, 3634584; 526261,
3634587; 526270, 3634588; 526277,
3634588; 526310, 3634612; 526318,
3634617; 526320, 3634620; 526340,
3634682; 526341, 3634684; 526344,
3634694; 526348, 3634703; 526353,
3634712; 526358, 3634720; 526364,
3634728; 526370, 3634736; 526377,
3634743; 526385, 3634750; 526392,
3634756; 526400, 3634762; 526403,
3634764; 526449, 3634794; 526455,
3634797; 526464, 3634802; 526473,
3634806; 526483, 3634810; 526492,
3634812; 526502, 3634815; 526512,
3634816; 526522, 3634817; 526532,
3634818; 526542, 3634817; 526549,
3634817; 526586, 3634812; 526589,
3634812; 526598, 3634810; 526608,
3634808; 526618, 3634805; 526627,
3634802; 526636, 3634798; 526645,
3634793; 526653, 3634788; 526662,
3634782; 526669, 3634775; 526677,
3634769; 526683, 3634761; 526690,
3634754; 526695, 3634745; 526701,
3634737; 526705, 3634728; 526710,
3634719; 526712, 3634713; 526738,
3634641; 526739, 3634638; 526742,
3634628; 526744, 3634619; 526746,
3634609; 526747, 3634599; 526747,
3634589; 526747, 3634583; 526744,
3634492; 526761, 3634446; 526790,
3634400; 526792, 3634397; 526796,
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
3634389; 526797, 3634389; 526807,
3634393; 526814, 3634395; 526876,
3634412; 526877, 3634413; 526887,
3634415; 526897, 3634417; 526902,
3634417; 526973, 3634424; 526978,
3634425; 526988, 3634425; 526998,
3634425; 527008, 3634424; 527017,
3634422; 527027, 3634420; 527029,
3634419; 527087, 3634403; 527095,
3634401; 527104, 3634397; 527113,
3634393.
(iv) Subunit 3D. Land bounded by the
following UTM NAD27 coordinates
(E,N): 527888, 3635506; 527895,
3635500; 527901, 3635233; 527900,
3635233; 527896, 3635228; 527895,
3635227; 527494, 3635218; 527502,
3634924; 527484, 3634918; 527477,
3634916; 527467, 3634914; 527460,
3634912; 527393, 3634902; 527391,
3634902; 527381, 3634901; 527371,
3634901; 527314, 3634901; 527314,
3634901; 527304, 3634901; 527294,
3634902; 527284, 3634904; 527275,
3634906; 527265, 3634909; 527256,
3634912; 527247, 3634917; 527238,
3634921; 527229, 3634927; 527221,
3634932; 527214, 3634939; 527206,
3634945; 527200, 3634953; 527199,
3634953; 527164, 3634993; 527158,
3635001; 527152, 3635009; 527147,
3635017; 527142, 3635026; 527138,
3635035; 527134, 3635045; 527132,
3635054; 527129, 3635064; 527128,
3635074; 527127, 3635076; 527120,
3635142; 527119, 3635150; 527119,
3635160; 527119, 3635170; 527120,
3635180; 527121, 3635189; 527124,
3635199; 527127, 3635209; 527130,
3635218; 527130, 3635219; 527172,
3635317; 527176, 3635326; 527180,
3635335; 527186, 3635343; 527191,
3635351; 527196, 3635357; 527263,
3635436; 527265, 3635438; 527272,
3635445; 527279, 3635452; 527285,
3635457; 527376, 3635529; 527378,
3635530; 527386, 3635536; 527395,
3635541; 527403, 3635546; 527413,
3635550; 527422, 3635554; 527430,
3635556; 527514, 3635580; 527516,
3635580; 527525, 3635582; 527535,
3635584; 527545, 3635585; 527555,
3635585; 527565, 3635585; 527566,
3635585; 527661, 3635578; 527671,
3635577; 527680, 3635576; 527690,
3635573; 527763, 3635554; 527823,
3635540; 527827, 3635539; 527837,
3635536; 527846, 3635532; 527855,
3635528; 527864, 3635524; 527872,
3635518; 527881, 3635513; 527888,
3635506.
(v) Subunit 3E. Land bounded by the
following UTM NAD27 coordinates
(E,N): 529317, 3636146; 529307,
3636146; 529297, 3636146; 529297,
3636146; 529284, 3636147; 529274,
3636148; 529264, 3636149; 529260,
3636150; 529249, 3636153; 529243,
3636154; 529233, 3636157; 529224,
PO 00000
Frm 00036
Fmt 4701
Sfmt 4702
3636161; 529215, 3636165; 529210,
3636167; 529197, 3636175; 529193,
3636177; 529184, 3636182; 529176,
3636188; 529168, 3636194; 529161,
3636201; 529154, 3636208; 529148,
3636216; 529143, 3636223; 529135,
3636235; 529134, 3636236; 529129,
3636245; 529124, 3636253; 529120,
3636263; 529116, 3636272; 529114,
3636279; 529111, 3636290; 529110,
3636292; 529108, 3636302; 529107,
3636311; 529106, 3636321; 529105,
3636331; 529106, 3636341; 529107,
3636351; 529107, 3636356; 529110,
3636370; 529111, 3636376; 529113,
3636386; 529116, 3636395; 529119,
3636405; 529123, 3636413; 529129,
3636426; 529130, 3636427; 529134,
3636435; 529140, 3636444; 529145,
3636451; 529160, 3636471; 529161,
3636472; 529167, 3636480; 529174,
3636487; 529181, 3636494; 529189,
3636500; 529195, 3636505; 529214,
3636518; 529216, 3636519; 529224,
3636524; 529233, 3636529; 529242,
3636533; 529251, 3636537; 529258,
3636539; 529276, 3636544; 529279,
3636544; 529288, 3636547; 529297,
3636548; 529319, 3636551; 529321,
3636552; 529331, 3636553; 529340,
3636553; 529350, 3636553; 529360,
3636552; 529370, 3636550; 529373,
3636549; 529388, 3636546; 529394,
3636544; 529404, 3636542; 529413,
3636538; 529416, 3636537; 529428,
3636532; 529434, 3636529; 529443,
3636524; 529451, 3636519; 529459,
3636513; 529467, 3636507; 529474,
3636500; 529481, 3636493; 529483,
3636490; 529495, 3636476; 529499,
3636471; 529505, 3636463; 529510,
3636454; 529515, 3636446; 529519,
3636437; 529523, 3636427; 529525,
3636420; 529531, 3636398; 529532,
3636396; 529534, 3636386; 529536,
3636376; 529537, 3636366; 529537,
3636356; 529537, 3636356; 529537,
3636345; 529537, 3636336; 529536,
3636326; 529534, 3636316; 529532,
3636306; 529529, 3636296; 529525,
3636287; 529521, 3636278; 529519,
3636273; 529512, 3636262; 529510,
3636258; 529505, 3636249; 529499,
3636241; 529493, 3636233; 529492,
3636233; 529480, 3636219; 529474,
3636212; 529466, 3636205; 529459,
3636199; 529451, 3636193; 529442,
3636188; 529439, 3636186; 529419,
3636175; 529414, 3636173; 529405,
3636169; 529402, 3636167; 529379,
3636159; 529373, 3636156; 529363,
3636153; 529354, 3636151; 529347,
3636150; 529330, 3636147; 529327,
3636147; 529317, 3636146.
(vi) Subunit 3F. Land bounded by the
following UTM NAD27 coordinates
(E,N): 530313, 3635051; 530303,
3635049; 530293, 3635047; 530291,
E:\FR\FM\14MRP2.SGM
14MRP2
cprice-sewell on PROD1PC66 with PROPOSALS2
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
3635047; 530281, 3635046; 530273,
3635045; 530263, 3635044; 530253,
3635045; 530243, 3635046; 530241,
3635046; 530234, 3635047; 530225,
3635049; 530215, 3635051; 530206,
3635054; 530196, 3635057; 530187,
3635061; 530179, 3635066; 530170,
3635071; 530162, 3635077; 530154,
3635083; 530154, 3635083; 530143,
3635093; 530136, 3635100; 530129,
3635107; 530123, 3635115; 530117,
3635123; 530111, 3635132; 530107,
3635141; 530103, 3635150; 530101,
3635153; 530096, 3635166; 530094,
3635173; 530091, 3635182; 530089,
3635192; 530087, 3635202; 530086,
3635212; 530086, 3635218; 530085,
3635235; 530085, 3635238; 530086,
3635248; 530087, 3635258; 530087,
3635259; 530089, 3635277; 530091,
3635285; 530093, 3635295; 530096,
3635304; 530099, 3635314; 530100,
3635316; 530109, 3635336; 530112,
3635344; 530117, 3635352; 530122,
3635361; 530128, 3635369; 530133,
3635374; 530140, 3635383; 530142,
3635386; 530149, 3635393; 530156,
3635400; 530164, 3635406; 530172,
3635412; 530176, 3635415; 530186,
3635421; 530191, 3635424; 530200,
3635428; 530209, 3635432; 530218,
3635436; 530228, 3635439; 530237,
3635441; 530246, 3635443; 530255,
3635444; 530257, 3635444; 530265,
3635445; 530264, 3635448; 530263,
3635458; 530263, 3635458; 530261,
3635472; 530260, 3635481; 530260,
3635491; 530260, 3635501; 530261,
3635510; 530262, 3635522; 530263,
3635523; 530264, 3635533; 530266,
3635542; 530269, 3635552; 530273,
3635561; 530275, 3635567; 530279,
3635575; 530281, 3635578; 530291,
3635578; 530311, 3635593; 530327,
3635609; 530347, 3635630; 530361,
3635647; 530364, 3635658; 530367,
3635660; 530377, 3635663; 530386,
3635666; 530386, 3635666; 530395,
3635669; 530405, 3635672; 530415,
3635673; 530425, 3635674; 530432,
3635674; 530446, 3635675; 530449,
3635675; 530459, 3635674; 530469,
3635673; 530479, 3635672; 530488,
3635670; 530491, 3635669; 530507,
3635664; 530514, 3635662; 530523,
3635659; 530532, 3635655; 530541,
3635650; 530549, 3635645; 530558,
3635639; 530565, 3635632; 530571,
3635627; 530581, 3635617; 530582,
3635616; 530589, 3635609; 530595,
3635601; 530601, 3635593; 530606,
3635585; 530611, 3635576; 530613,
3635571; 530618, 3635560; 530620,
3635556; 530628, 3635562; 530636,
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
3635567; 530645, 3635572; 530649,
3635574; 530671, 3635584; 530677,
3635587; 530686, 3635590; 530696,
3635593; 530705, 3635595; 530713,
3635597; 530733, 3635600; 530735,
3635600; 530729, 3635610; 530729,
3635611; 530725, 3635620; 530721,
3635630; 530718, 3635639; 530717,
3635643; 530715, 3635652; 530712,
3635655; 530705, 3635663; 530698,
3635670; 530693, 3635678; 530691,
3635681; 530686, 3635689; 530682,
3635695; 530677, 3635704; 530673,
3635713; 530670, 3635722; 530668,
3635728; 530665, 3635738; 530664,
3635742; 530662, 3635751; 530660,
3635761; 530659, 3635771; 530659,
3635781; 530659, 3635791; 530659,
3635792; 530655, 3635802; 530654,
3635804; 530651, 3635813; 530648,
3635823; 530646, 3635833; 530644,
3635842; 530644, 3635846; 530642,
3635857; 530642, 3635864; 530641,
3635874; 530642, 3635884; 530643,
3635894; 530643, 3635898; 530645,
3635906; 530646, 3635912; 530648,
3635922; 530651, 3635932; 530654,
3635941; 530656, 3635944; 530660,
3635953; 530663, 3635959; 530667,
3635968; 530673, 3635976; 530673,
3635977; 530679, 3635985; 530684,
3635992; 530690, 3636000; 530697,
3636007; 530704, 3636014; 530707,
3636017; 530717, 3636024; 530721,
3636028; 530729, 3636034; 530738,
3636039; 530741, 3636041; 530747,
3636044; 530752, 3636047; 530761,
3636051; 530771, 3636054; 530780,
3636057; 530781, 3636058; 530790,
3636060; 530799, 3636062; 530809,
3636064; 530819, 3636065; 530829,
3636065; 530833, 3636065; 530844,
3636065; 530850, 3636064; 530860,
3636063; 530870, 3636062; 530880,
3636059; 530889, 3636057; 530899,
3636053; 530906, 3636050; 530906,
3636050; 530915, 3636046; 530920,
3636043; 530923, 3636048; 530929,
3636059; 530930, 3636060; 530935,
3636069; 530941, 3636077; 530947,
3636085; 530954, 3636092; 530961,
3636099; 530969, 3636105; 530974,
3636108; 530988, 3636118; 530991,
3636121; 531000, 3636126; 531008,
3636131; 531018, 3636135; 531027,
3636138; 531036, 3636141; 531046,
3636144; 531056, 3636145; 531066,
3636146; 531073, 3636146; 531089,
3636147; 531092, 3636147; 531102,
3636146; 531112, 3636145; 531122,
3636144; 531132, 3636142; 531141,
3636139; 531149, 3636136; 531163,
3636130; 531164, 3636130; 531173,
3636125; 531182, 3636121; 531191,
PO 00000
Frm 00037
Fmt 4701
Sfmt 4702
11981
3636116; 531199, 3636110; 531206,
3636103; 531213, 3636097; 531223,
3636087; 531224, 3636086; 531231,
3636079; 531237, 3636071; 531243,
3636063; 531248, 3636055; 531253,
3636046; 531257, 3636037; 531260,
3636028; 531262, 3636024; 531268,
3636003; 531270, 3635997; 531272,
3635987; 531274, 3635978; 531275,
3635968; 531275, 3635958; 531275,
3635951; 531274, 3635927; 531274,
3635925; 531272, 3635895; 531272,
3635893; 531271, 3635883; 531269,
3635873; 531267, 3635864; 531264,
3635854; 531257, 3635832; 531257,
3635832; 531253, 3635822; 531249,
3635813; 531244, 3635804; 531239,
3635796; 531233, 3635788; 531230,
3635784; 531224, 3635776; 531221,
3635772; 531214, 3635765; 531206,
3635758; 531206, 3635758; 531206,
3635755; 531203, 3635746; 531203,
3635744; 531200, 3635734; 531201,
3635728; 531201, 3635727; 531202,
3635717; 531202, 3635707; 531202,
3635697; 531201, 3635687; 531198,
3635665; 531198, 3635665; 531197,
3635655; 531194, 3635645; 531191,
3635636; 531188, 3635626; 531184,
3635617; 531183, 3635616; 531171,
3635593; 531167, 3635585; 531162,
3635576; 531156, 3635568; 531150,
3635560; 531143, 3635553; 531122,
3635532; 531122, 3635532; 531115,
3635525; 531107, 3635519; 531105,
3635517; 531085, 3635503; 531071,
3635491; 531069, 3635489; 531060,
3635483; 531052, 3635478; 531043,
3635473; 531034, 3635469; 531031,
3635468; 531014, 3635462; 531008,
3635460; 530999, 3635457; 530989,
3635454; 530979, 3635453; 530969,
3635452; 530959, 3635451; 530954,
3635452; 530940, 3635452; 530936,
3635452; 530936, 3635452; 530938,
3635442; 530940, 3635432; 530941,
3635422; 530941, 3635412; 530941,
3635402; 530940, 3635392; 530938,
3635383; 530938, 3635379; 530930,
3635343; 530928, 3635337; 530925,
3635327; 530922, 3635319; 530910,
3635289; 530910, 3635288; 530906,
3635279; 530904, 3635275; 530888,
3635245; 530885, 3635240; 530880,
3635232; 530828, 3635152; 530827,
3635151; 530824, 3635147; 530633,
3635163; 530319, 3635191; 530319,
3635116; 530319, 3635053; 530313,
3635051.
(vii) Note: Map of Unit 3, subunits 3A,
3B, 3C, 3D, 3E, and 3F (Map 4), follows:
BILLING CODE 4310–55–P
E:\FR\FM\14MRP2.SGM
14MRP2
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
BILLING CODE 4310–55–C
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
PO 00000
Frm 00038
Fmt 4701
Sfmt 4702
E:\FR\FM\14MRP2.SGM
14MRP2
EP14MR07.003
cprice-sewell on PROD1PC66 with PROPOSALS2
11982
cprice-sewell on PROD1PC66 with PROPOSALS2
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
(9) Unit 4: San Diego County,
California. From USGS 1:24,000
quadrangle maps Alpine and Dulzura.
(i) Subunit 4A. Land bounded by the
following UTM NAD27 coordinates
(E,N): 512236, 3624084; 512233,
3624084; 512230, 3624084; 512227,
3624084; 512224, 3624084; 512221,
3624085; 512218, 3624085; 512216,
3624085; 512213, 3624085; 512210,
3624086; 512207, 3624086; 512204,
3624087; 512201, 3624087; 512198,
3624088; 512196, 3624089; 512193,
3624089; 512190, 3624090; 512187,
3624091; 512184, 3624092; 512182,
3624093; 512179, 3624094; 512176,
3624095; 512174, 3624096; 512171,
3624097; 512168, 3624098; 512166,
3624100; 512163, 3624101; 512161,
3624102; 512158, 3624104; 512155,
3624105; 512153, 3624107; 512151,
3624108; 512148, 3624110; 512146,
3624112; 512143, 3624113; 512141,
3624115; 512139, 3624117; 512136,
3624119; 512134, 3624120; 512132,
3624122; 512130, 3624124; 512128,
3624126; 512126, 3624128; 512124,
3624130; 512122, 3624132; 512120,
3624135; 512118, 3624137; 512116,
3624139; 512114, 3624141; 512112,
3624143; 512110, 3624146; 512109,
3624148; 512107, 3624151; 512105,
3624153; 512104, 3624155; 512102,
3624158; 512101, 3624160; 512099,
3624163; 512098, 3624165; 512097,
3624168; 512095, 3624171; 512094,
3624173; 512093, 3624176; 512092,
3624179; 512091, 3624181; 512090,
3624184; 512089, 3624187; 512088,
3624189; 512087, 3624192; 512086,
3624195; 512085, 3624198; 512085,
3624201; 512084, 3624203; 512083,
3624206; 512083, 3624209; 512082,
3624212; 512082, 3624215; 512082,
3624218; 512081, 3624221; 512081,
3624224; 512081, 3624226; 512081,
3624229; 512081, 3624232; 512080,
3624235; 512080, 3624238; 512081,
3624241; 512081, 3624244; 512081,
3624247; 512081, 3624250; 512081,
3624253; 512082, 3624255; 512082,
3624258; 512082, 3624261; 512083,
3624264; 512083, 3624267; 512084,
3624270; 512085, 3624273; 512085,
3624275; 512086, 3624278; 512087,
3624281; 512088, 3624284; 512089,
3624286; 512090, 3624289; 512091,
3624292; 512092, 3624295; 512093,
3624297; 512094, 3624300; 512095,
3624303; 512097, 3624305; 512098,
3624308; 512099, 3624310; 512101,
3624313; 512102, 3624315; 512104,
3624318; 512105, 3624320; 512107,
3624323; 512109, 3624325; 512110,
3624327; 512112, 3624330; 512114,
3624332; 512116, 3624334; 512118,
3624336; 512120, 3624339; 512122,
3624341; 512124, 3624343; 512126,
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
3624345; 512128, 3624347; 512130,
3624349; 512132, 3624351; 512134,
3624353; 512136, 3624355; 512139,
3624356; 512141, 3624358; 512143,
3624360; 512146, 3624362; 512148,
3624363; 512151, 3624365; 512153,
3624366; 512155, 3624368; 512158,
3624369; 512161, 3624371; 512163,
3624372; 512166, 3624373; 512168,
3624375; 512171, 3624376; 512174,
3624377; 512176, 3624378; 512179,
3624379; 512182, 3624380; 512184,
3624381; 512187, 3624382; 512190,
3624383; 512193, 3624384; 512196,
3624384; 512198, 3624385; 512201,
3624386; 512204, 3624386; 512207,
3624387; 512210, 3624387; 512213,
3624388; 512216, 3624388; 512218,
3624388; 512221, 3624389; 512224,
3624389; 512227, 3624389; 512230,
3624389; 512233, 3624389; 512236,
3624389; 512239, 3624389; 512242,
3624389; 512245, 3624389; 512247,
3624388; 512250, 3624388; 512253,
3624388; 512256, 3624387; 512259,
3624387; 512262, 3624386; 512265,
3624386; 512267, 3624385; 512270,
3624384; 512273, 3624384; 512276,
3624383; 512279, 3624382; 512281,
3624381; 512284, 3624380; 512287,
3624379; 512290, 3624378; 512292,
3624377; 512295, 3624376; 512298,
3624375; 512300, 3624373; 512303,
3624372; 512305, 3624371; 512308,
3624369; 512310, 3624368; 512313,
3624366; 512315, 3624365; 512318,
3624363; 512320, 3624362; 512323,
3624360; 512325, 3624358; 512327,
3624356; 512329, 3624355; 512332,
3624353; 512334, 3624351; 512336,
3624349; 512338, 3624347; 512340,
3624345; 512342, 3624343; 512344,
3624341; 512346, 3624339; 512348,
3624336; 512350, 3624334; 512352,
3624332; 512354, 3624330; 512355,
3624327; 512357, 3624325; 512359,
3624323; 512360, 3624320; 512362,
3624318; 512364, 3624315; 512365,
3624313; 512366, 3624310; 512368,
3624308; 512369, 3624305; 512370,
3624303; 512372, 3624300; 512373,
3624297; 512374, 3624295; 512375,
3624292; 512376, 3624289; 512377,
3624286; 512378, 3624284; 512379,
3624281; 512380, 3624278; 512380,
3624275; 512381, 3624273; 512382,
3624270; 512382, 3624267; 512383,
3624264; 512383, 3624261; 512384,
3624258; 512384, 3624255; 512385,
3624253; 512385, 3624250; 512385,
3624247; 512385, 3624244; 512385,
3624241; 512385, 3624238; 512385,
3624235; 512385, 3624232; 512385,
3624229; 512385, 3624226; 512385,
3624224; 512385, 3624221; 512384,
3624218; 512384, 3624215; 512383,
3624212; 512383, 3624209; 512382,
3624206; 512382, 3624203; 512381,
PO 00000
Frm 00039
Fmt 4701
Sfmt 4702
11983
3624201; 512380, 3624198; 512380,
3624195; 512379, 3624192; 512378,
3624189; 512377, 3624187; 512376,
3624184; 512375, 3624181; 512374,
3624179; 512373, 3624176; 512372,
3624173; 512370, 3624171; 512369,
3624168; 512368, 3624165; 512366,
3624163; 512365, 3624160; 512364,
3624158; 512362, 3624155; 512360,
3624153; 512359, 3624151; 512357,
3624148; 512355, 3624146; 512354,
3624143; 512352, 3624141; 512350,
3624139; 512348, 3624137; 512346,
3624135; 512344, 3624132; 512342,
3624130; 512340, 3624128; 512338,
3624126; 512336, 3624124; 512334,
3624122; 512332, 3624120; 512329,
3624119; 512327, 3624117; 512325,
3624115; 512323, 3624113; 512320,
3624112; 512318, 3624110; 512315,
3624108; 512313, 3624107; 512310,
3624105; 512308, 3624104; 512305,
3624102; 512303, 3624101; 512300,
3624100; 512298, 3624098; 512295,
3624097; 512292, 3624096; 512290,
3624095; 512287, 3624094; 512284,
3624093; 512281, 3624092; 512279,
3624091; 512276, 3624090; 512273,
3624089; 512270, 3624089; 512267,
3624088; 512265, 3624087; 512262,
3624087; 512259, 3624086; 512256,
3624086; 512253, 3624085; 512250,
3624085; 512247, 3624085; 512245,
3624085; 512242, 3624084; 512239,
3624084; 512236, 3624084. Land
bounded by 512297, 3623324; 512272,
3623323; 512234, 3623334; 512185,
3623361; 512163, 3623400; 512214,
3623403; 512216, 3623412; 512233,
3623405; 512281, 3623398; 512302,
3623368; 512301, 3623330; 512297,
3623324.
(ii) Subunit 4B. Land bounded by the
following UTM NAD27 coordinates
(E,N): 513127, 3624170; 513130,
3624169; 513133, 3624169; 513136,
3624169; 513139, 3624168; 513142,
3624168; 513144, 3624168; 513147,
3624167; 513150, 3624166; 513153,
3624166; 513156, 3624165; 513159,
3624164; 513161, 3624164; 513164,
3624163; 513167, 3624162; 513170,
3624161; 513172, 3624160; 513175,
3624159; 513178, 3624158; 513179,
3624157; 513186, 3624157; 513196,
3624156; 513205, 3624154; 513205,
3624154; 513211, 3624153; 513224,
3624150; 513228, 3624149; 513237,
3624146; 513246, 3624143; 513255,
3624139; 513264, 3624134; 513273,
3624129; 513281, 3624123; 513289,
3624116; 513296, 3624110; 513303,
3624102; 513303, 3624102; 513306,
3624098; 513309, 3624096; 513317,
3624089; 513323, 3624081; 513330,
3624074; 513332, 3624071; 513337,
3624069; 513341, 3624067; 513350,
3624063; 513359, 3624058; 513367,
E:\FR\FM\14MRP2.SGM
14MRP2
cprice-sewell on PROD1PC66 with PROPOSALS2
11984
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
3624053; 513371, 3624050; 513378,
3624046; 513382, 3624042; 513387,
3624038; 513401, 3624027; 513404,
3624024; 513411, 3624018; 513418,
3624010; 513424, 3624003; 513430,
3623994; 513431, 3623993; 513438,
3623983; 513442, 3623976; 513447,
3623967; 513451, 3623958; 513454,
3623948; 513457, 3623939; 513459,
3623929; 513461, 3623919; 513461,
3623919; 513463, 3623905; 513464,
3623895; 513464, 3623885; 513464,
3623878; 513463, 3623853; 513463,
3623850; 513462, 3623841; 513461,
3623832; 513461, 3623830; 513459,
3623820; 513457, 3623811; 513456,
3623806; 513447, 3623778; 513446,
3623773; 513442, 3623763; 513442,
3623763; 513454, 3623761; 513454,
3623761; 513464, 3623760; 513474,
3623757; 513479, 3623756; 513508,
3623747; 513513, 3623745; 513522,
3623742; 513531, 3623738; 513540,
3623733; 513543, 3623732; 513552,
3623726; 513558, 3623722; 513566,
3623717; 513567, 3623716; 513577,
3623708; 513584, 3623702; 513591,
3623695; 513598, 3623688; 513603,
3623682; 513614, 3623668; 513615,
3623667; 513621, 3623659; 513626,
3623650; 513631, 3623642; 513632,
3623640; 513637, 3623630; 513640,
3623622; 513643, 3623613; 513646,
3623603; 513648, 3623594; 513650,
3623584; 513651, 3623574; 513651,
3623564; 513651, 3623554; 513650,
3623544; 513650, 3623541; 513649,
3623533; 513647, 3623526; 513645,
3623516; 513642, 3623507; 513642,
3623506; 513639, 3623497; 513636,
3623489; 513632, 3623480; 513627,
3623471; 513622, 3623462; 513617,
3623456; 513610, 3623446; 513608,
3623445; 513602, 3623437; 513595,
3623430; 513588, 3623423; 513580,
3623416; 513572, 3623411; 513564,
3623405; 513555, 3623401; 513546,
3623396; 513542, 3623395; 513534,
3623392; 513533, 3623391; 513517,
3623386; 513513, 3623384; 513504,
3623381; 513494, 3623379; 513484,
3623378; 513474, 3623377; 513464,
3623376; 513454, 3623377; 513444,
3623378; 513435, 3623379; 513426,
3623381; 513419, 3623383; 513418,
3623383; 513415, 3623384; 513408,
3623385; 513405, 3623386; 513397,
3623388; 513379, 3623392; 513376,
3623393; 513366, 3623393; 513362,
3623394; 513358, 3623394; 513354,
3623394; 513353, 3623394; 513349,
3623395; 513337, 3623396; 513335,
3623396; 513331, 3623396; 513315,
3623397; 513312, 3623397; 513307,
3623397; 513303, 3623398; 513286,
3623390; 513285, 3623389; 513279,
3623385; 513270, 3623381; 513270,
3623380; 513269, 3623380; 513262,
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
3623373; 513254, 3623366; 513246,
3623361; 513239, 3623356; 513237,
3623355; 513230, 3623349; 513221,
3623343; 513215, 3623339; 513213,
3623337; 513213, 3623337; 513215,
3623335; 513216, 3623332; 513217,
3623330; 513219, 3623327; 513220,
3623324; 513221, 3623322; 513222,
3623319; 513223, 3623316; 513224,
3623314; 513225, 3623311; 513226,
3623308; 513227, 3623305; 513227,
3623302; 513228, 3623300; 513229,
3623297; 513229, 3623294; 513230,
3623291; 513230, 3623288; 513231,
3623285; 513231, 3623282; 513231,
3623280; 513232, 3623277; 513232,
3623274; 513232, 3623271; 513232,
3623268; 513232, 3623265; 513232,
3623262; 513232, 3623259; 513232,
3623256; 513232, 3623253; 513232,
3623251; 513231, 3623248; 513231,
3623245; 513231, 3623242; 513230,
3623239; 513230, 3623236; 513229,
3623233; 513229, 3623231; 513228,
3623228; 513227, 3623225; 513227,
3623222; 513226, 3623219; 513225,
3623217; 513224, 3623214; 513223,
3623211; 513222, 3623208; 513221,
3623206; 513220, 3623203; 513219,
3623200; 513217, 3623198; 513216,
3623195; 513215, 3623192; 513213,
3623190; 513212, 3623187; 513210,
3623185; 513209, 3623182; 513207,
3623180; 513206, 3623178; 513204,
3623175; 513202, 3623173; 513201,
3623171; 513199, 3623168; 513197,
3623166; 513195, 3623164; 513193,
3623162; 513191, 3623159; 513189,
3623157; 513187, 3623155; 513185,
3623153; 513183, 3623151; 513181,
3623149; 513179, 3623147; 513176,
3623146; 513174, 3623144; 513172,
3623142; 513169, 3623140; 513167,
3623139; 513165, 3623137; 513162,
3623135; 513160, 3623134; 513157,
3623132; 513155, 3623131; 513152,
3623129; 513150, 3623128; 513147,
3623127; 513144, 3623126; 513142,
3623124; 513139, 3623123; 513136,
3623122; 513134, 3623121; 513131,
3623120; 513128, 3623119; 513126,
3623118; 513123, 3623117; 513120,
3623117; 513117, 3623116; 513114,
3623115; 513111, 3623114; 513109,
3623114; 513106, 3623113; 513103,
3623113; 513100, 3623112; 513097,
3623112; 513094, 3623112; 513091,
3623112; 513088, 3623111; 513086,
3623111; 513083, 3623111; 513080,
3623111; 513077, 3623111; 513074,
3623111; 513071, 3623111; 513068,
3623112; 513065, 3623112; 513062,
3623112; 513060, 3623112; 513057,
3623113; 513054, 3623113; 513051,
3623114; 513048, 3623114; 513045,
3623115; 513042, 3623116; 513040,
3623117; 513037, 3623117; 513034,
3623118; 513031, 3623119; 513029,
PO 00000
Frm 00040
Fmt 4701
Sfmt 4702
3623120; 513026, 3623121; 513023,
3623122; 513021, 3623123; 513021,
3623122; 513020, 3623118; 513019,
3623114; 513019, 3623111; 513017,
3623106; 513014, 3623098; 513009,
3623092; 513004, 3623092; 512998,
3623094; 512988, 3623097; 512982,
3623097; 512978, 3623100; 512974,
3623104; 512970, 3623107; 512966,
3623113; 512964, 3623115; 512962,
3623116; 512957, 3623121; 512952,
3623126; 512948, 3623137; 512948,
3623143; 512948, 3623148; 512949,
3623161; 512950, 3623163; 512952,
3623168; 512955, 3623172; 512956,
3623174; 512956, 3623175; 512954,
3623178; 512952, 3623180; 512951,
3623182; 512949, 3623185; 512948,
3623187; 512946, 3623190; 512945,
3623192; 512944, 3623195; 512942,
3623198; 512941, 3623200; 512940,
3623203; 512939, 3623206; 512938,
3623208; 512937, 3623211; 512936,
3623214; 512935, 3623217; 512934,
3623219; 512933, 3623222; 512932,
3623225; 512932, 3623228; 512931,
3623231; 512930, 3623233; 512930,
3623236; 512929, 3623239; 512929,
3623242; 512928, 3623245; 512928,
3623248; 512928, 3623251; 512928,
3623253; 512927, 3623256; 512927,
3623259; 512927, 3623262; 512927,
3623265; 512927, 3623268; 512927,
3623271; 512928, 3623274; 512928,
3623277; 512928, 3623277; 512922,
3623280; 512913, 3623285; 512906,
3623289; 512900, 3623293; 512898,
3623294; 512894, 3623297; 512888,
3623301; 512884, 3623305; 512876,
3623311; 512869, 3623318; 512862,
3623325; 512861, 3623326; 512859,
3623328; 512853, 3623334; 512850,
3623338; 512844, 3623345; 512838,
3623353; 512833, 3623361; 512832,
3623364; 512831, 3623365; 512826,
3623374; 512822, 3623383; 512820,
3623389; 512819, 3623391; 512818,
3623394; 512815, 3623404; 512813,
3623413; 512811, 3623423; 512810,
3623433; 512810, 3623442; 512810,
3623449; 512810, 3623451; 512810,
3623460; 512811, 3623470; 512811,
3623471; 512812, 3623476; 512813,
3623485; 512816, 3623495; 512819,
3623504; 512820, 3623507; 512821,
3623512; 512822, 3623513; 512823,
3623516; 512825, 3623522; 512829,
3623531; 512834, 3623540; 512839,
3623548; 512845, 3623556; 512848,
3623560; 512854, 3623567; 512857,
3623571; 512864, 3623579; 512871,
3623585; 512879, 3623592; 512880,
3623592; 512890, 3623600; 512897,
3623605; 512906, 3623610; 512907,
3623611; 512907, 3623611; 512908,
3623612; 512913, 3623615; 512922,
3623621; 512923, 3623622; 512929,
3623626; 512940, 3623633; 512943,
E:\FR\FM\14MRP2.SGM
14MRP2
cprice-sewell on PROD1PC66 with PROPOSALS2
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
3623634; 512951, 3623639; 512955,
3623640; 512966, 3623645; 512967,
3623646; 512969, 3623648; 512971,
3623649; 512970, 3623649; 512969,
3623652; 512969, 3623655; 512968,
3623657; 512967, 3623660; 512966,
3623663; 512966, 3623666; 512965,
3623669; 512964, 3623672; 512964,
3623674; 512963, 3623677; 512963,
3623680; 512963, 3623683; 512963,
3623686; 512962, 3623689; 512962,
3623692; 512962, 3623695; 512962,
3623698; 512962, 3623700; 512962,
3623703; 512962, 3623706; 512962,
3623709; 512963, 3623712; 512963,
3623715; 512963, 3623718; 512963,
3623721; 512964, 3623724; 512964,
3623726; 512965, 3623729; 512966,
3623732; 512966, 3623735; 512967,
3623738; 512968, 3623741; 512969,
3623743; 512969, 3623746; 512970,
3623749; 512971, 3623752; 512972,
3623754; 512973, 3623757; 512975,
3623760; 512976, 3623762; 512977,
3623765; 512978, 3623768; 512980,
3623770; 512981, 3623773; 512982,
3623775; 512984, 3623778; 512985,
3623780; 512987, 3623783; 512989,
3623785; 512990, 3623787; 512992,
3623789; 512990, 3623793; 512986,
3623801; 512986, 3623802; 512983,
3623811; 512980, 3623821; 512978,
3623830; 512977, 3623833; 512976,
3623838; 512971, 3623860; 512969,
3623868; 512968, 3623870; 512967,
3623878; 512966, 3623885; 512965,
3623895; 512965, 3623904; 512965,
3623910; 512965, 3623918; 512965,
3623919; 512965, 3623929; 512965,
3623934; 512966, 3623945; 512967,
3623951; 512968, 3623957; 512968,
3623958; 512970, 3623970; 512971,
3623979; 512970, 3623981; 512970,
3623984; 512969, 3623987; 512968,
3623990; 512968, 3623993; 512967,
3623996; 512967, 3623999; 512967,
3624001; 512966, 3624004; 512966,
3624007; 512966, 3624010; 512966,
3624013; 512966, 3624016; 512966,
3624019; 512966, 3624022; 512966,
3624025; 512966, 3624027; 512966,
3624030; 512967, 3624033; 512967,
3624036; 512967, 3624039; 512968,
3624042; 512968, 3624045; 512969,
3624048; 512970, 3624050; 512970,
3624053; 512971, 3624056; 512972,
3624059; 512973, 3624062; 512973,
3624064; 512974, 3624067; 512975,
3624070; 512976, 3624073; 512977,
3624075; 512979, 3624078; 512980,
3624081; 512981, 3624083; 512982,
3624086; 512984, 3624088; 512985,
3624091; 512986, 3624094; 512988,
3624096; 512989, 3624099; 512991,
3624101; 512993, 3624103; 512994,
3624106; 512996, 3624108; 512998,
3624110; 512999, 3624113; 513001,
3624115; 513003, 3624117; 513005,
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
3624119; 513007, 3624122; 513009,
3624124; 513011, 3624126; 513013,
3624128; 513015, 3624130; 513017,
3624132; 513020, 3624134; 513022,
3624135; 513024, 3624137; 513026,
3624139; 513029, 3624141; 513031,
3624142; 513034, 3624144; 513036,
3624146; 513038, 3624147; 513041,
3624149; 513043, 3624150; 513046,
3624152; 513049, 3624153; 513051,
3624154; 513054, 3624155; 513056,
3624157; 513059, 3624158; 513062,
3624159; 513064, 3624160; 513067,
3624161; 513070, 3624162; 513073,
3624163; 513075, 3624164; 513078,
3624164; 513081, 3624165; 513084,
3624166; 513087, 3624166; 513090,
3624167; 513092, 3624168; 513095,
3624168; 513098, 3624168; 513101,
3624169; 513104, 3624169; 513107,
3624169; 513110, 3624170; 513113,
3624170; 513116, 3624170; 513118,
3624170; 513121, 3624170; 513124,
3624170; 513127, 3624170. Land
bounded by 512989, 3622663; 512986,
3622663; 512984, 3622663; 512981,
3622663; 512978, 3622663; 512975,
3622663; 512972, 3622663; 512969,
3622664; 512966, 3622664; 512963,
3622664; 512960, 3622665; 512958,
3622665; 512955, 3622666; 512952,
3622666; 512949, 3622667; 512946,
3622668; 512943, 3622669; 512941,
3622670; 512938, 3622670; 512935,
3622671; 512932, 3622672; 512930,
3622673; 512927, 3622675; 512924,
3622676; 512922, 3622677; 512919,
3622678; 512917, 3622679; 512914,
3622681; 512911, 3622682; 512909,
3622684; 512906, 3622685; 512904,
3622687; 512902, 3622688; 512899,
3622690; 512897, 3622692; 512894,
3622693; 512892, 3622695; 512890,
3622697; 512888, 3622699; 512885,
3622701; 512883, 3622703; 512881,
3622705; 512879, 3622707; 512877,
3622709; 512875, 3622711; 512873,
3622713; 512871, 3622715; 512869,
3622717; 512867, 3622720; 512866,
3622722; 512864, 3622724; 512862,
3622727; 512861, 3622729; 512859,
3622731; 512857, 3622734; 512856,
3622736; 512854, 3622739; 512853,
3622741; 512852, 3622744; 512850,
3622746; 512849, 3622749; 512848,
3622752; 512847, 3622754; 512845,
3622757; 512844, 3622760; 512843,
3622762; 512842, 3622765; 512841,
3622768; 512841, 3622771; 512840,
3622773; 512839, 3622776; 512838,
3622779; 512838, 3622782; 512837,
3622785; 512836, 3622788; 512836,
3622790; 512835, 3622793; 512835,
3622796; 512835, 3622799; 512834,
3622802; 512834, 3622805; 512834,
3622808; 512834, 3622811; 512834,
3622814; 512834, 3622816; 512834,
3622819; 512834, 3622822; 512834,
PO 00000
Frm 00041
Fmt 4701
Sfmt 4702
11985
3622825; 512834, 3622828; 512835,
3622831; 512835, 3622834; 512835,
3622837; 512836, 3622840; 512836,
3622842; 512837, 3622845; 512838,
3622848; 512838, 3622851; 512839,
3622854; 512840, 3622857; 512841,
3622859; 512841, 3622862; 512842,
3622865; 512843, 3622868; 512844,
3622870; 512845, 3622873; 512847,
3622876; 512848, 3622878; 512849,
3622881; 512850, 3622884; 512852,
3622886; 512853, 3622889; 512854,
3622891; 512856, 3622894; 512857,
3622896; 512859, 3622899; 512861,
3622901; 512862, 3622903; 512864,
3622906; 512866, 3622908; 512867,
3622910; 512869, 3622913; 512871,
3622915; 512873, 3622917; 512875,
3622919; 512877, 3622921; 512879,
3622923; 512881, 3622925; 512883,
3622927; 512885, 3622929; 512888,
3622931; 512890, 3622933; 512892,
3622935; 512894, 3622937; 512897,
3622938; 512899, 3622940; 512902,
3622942; 512904, 3622943; 512906,
3622945; 512909, 3622946; 512911,
3622948; 512914, 3622949; 512917,
3622951; 512919, 3622952; 512922,
3622953; 512924, 3622954; 512927,
3622955; 512930, 3622957; 512932,
3622958; 512935, 3622959; 512938,
3622960; 512941, 3622960; 512943,
3622961; 512946, 3622962; 512949,
3622963; 512952, 3622964; 512955,
3622964; 512958, 3622965; 512960,
3622965; 512963, 3622966; 512966,
3622966; 512969, 3622967; 512972,
3622967; 512975, 3622967; 512978,
3622967; 512981, 3622967; 512984,
3622967; 512986, 3622968; 512989,
3622967; 512992, 3622967; 512995,
3622967; 512998, 3622967; 513001,
3622967; 513004, 3622967; 513007,
3622966; 513010, 3622966; 513012,
3622965; 513015, 3622965; 513018,
3622964; 513021, 3622964; 513024,
3622963; 513027, 3622962; 513029,
3622961; 513032, 3622960; 513035,
3622960; 513038, 3622959; 513040,
3622958; 513043, 3622957; 513046,
3622955; 513048, 3622954; 513051,
3622953; 513054, 3622952; 513056,
3622951; 513059, 3622949; 513061,
3622948; 513064, 3622946; 513066,
3622945; 513069, 3622943; 513071,
3622942; 513074, 3622940; 513076,
3622938; 513078, 3622937; 513081,
3622935; 513083, 3622933; 513085,
3622931; 513087, 3622929; 513090,
3622927; 513092, 3622925; 513094,
3622923; 513096, 3622921; 513098,
3622919; 513100, 3622917; 513102,
3622915; 513104, 3622913; 513105,
3622910; 513107, 3622908; 513109,
3622906; 513111, 3622903; 513112,
3622901; 513114, 3622899; 513115,
3622896; 513117, 3622894; 513118,
3622891; 513120, 3622889; 513121,
E:\FR\FM\14MRP2.SGM
14MRP2
cprice-sewell on PROD1PC66 with PROPOSALS2
11986
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
3622886; 513123, 3622884; 513124,
3622881; 513125, 3622878; 513126,
3622876; 513127, 3622873; 513129,
3622870; 513130, 3622868; 513131,
3622865; 513131, 3622862; 513132,
3622859; 513133, 3622857; 513134,
3622854; 513135, 3622851; 513135,
3622848; 513136, 3622845; 513136,
3622842; 513137, 3622840; 513137,
3622837; 513138, 3622834; 513138,
3622831; 513138, 3622828; 513139,
3622825; 513139, 3622822; 513139,
3622819; 513139, 3622816; 513139,
3622814; 513139, 3622811; 513139,
3622808; 513139, 3622805; 513138,
3622802; 513138, 3622799; 513138,
3622796; 513137, 3622793; 513137,
3622790; 513136, 3622788; 513136,
3622785; 513135, 3622782; 513135,
3622779; 513134, 3622776; 513133,
3622773; 513132, 3622771; 513131,
3622768; 513131, 3622765; 513130,
3622762; 513129, 3622760; 513127,
3622757; 513126, 3622754; 513125,
3622752; 513124, 3622749; 513123,
3622746; 513121, 3622744; 513120,
3622741; 513118, 3622739; 513117,
3622736; 513115, 3622734; 513114,
3622731; 513112, 3622729; 513111,
3622727; 513109, 3622724; 513107,
3622722; 513105, 3622720; 513104,
3622717; 513102, 3622715; 513100,
3622713; 513098, 3622711; 513096,
3622709; 513094, 3622707; 513092,
3622705; 513090, 3622703; 513087,
3622701; 513085, 3622699; 513083,
3622697; 513081, 3622695; 513078,
3622693; 513076, 3622692; 513074,
3622690; 513071, 3622688; 513069,
3622687; 513066, 3622685; 513064,
3622684; 513061, 3622682; 513059,
3622681; 513056, 3622679; 513054,
3622678; 513051, 3622677; 513048,
3622676; 513046, 3622675; 513043,
3622673; 513040, 3622672; 513038,
3622671; 513035, 3622670; 513032,
3622670; 513029, 3622669; 513027,
3622668; 513024, 3622667; 513021,
3622666; 513018, 3622666; 513015,
3622665; 513012, 3622665; 513010,
3622664; 513007, 3622664; 513004,
3622664; 513001, 3622663; 512998,
3622663; 512995, 3622663; 512992,
3622663; 512989, 3622663.
(iii) Subunit 4C. Land bounded by the
following UTM NAD27 coordinates
(E,N): 512565, 3621839; 512559,
3621825; 512559, 3621825; 512556,
3621818; 512554, 3621813; 512552,
3621802; 512551, 3621798; 512548,
3621789; 512548, 3621789; 512549,
3621788; 512550, 3621786; 512552,
3621783; 512554, 3621781; 512555,
3621779; 512557, 3621776; 512558,
3621774; 512560, 3621771; 512561,
3621769; 512563, 3621766; 512564,
3621764; 512565, 3621761; 512567,
3621758; 512568, 3621756; 512569,
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
3621753; 512570, 3621750; 512571,
3621748; 512572, 3621745; 512573,
3621742; 512574, 3621739; 512575,
3621737; 512575, 3621734; 512576,
3621731; 512577, 3621728; 512577,
3621725; 512578, 3621722; 512578,
3621720; 512579, 3621717; 512579,
3621714; 512580, 3621711; 512580,
3621708; 512580, 3621705; 512580,
3621702; 512580, 3621699; 512580,
3621696; 512580, 3621694; 512580,
3621691; 512580, 3621688; 512580,
3621685; 512580, 3621682; 512580,
3621679; 512579, 3621676; 512579,
3621673; 512578, 3621670; 512578,
3621668; 512577, 3621665; 512577,
3621662; 512576, 3621659; 512575,
3621656; 512575, 3621653; 512574,
3621651; 512573, 3621648; 512572,
3621645; 512571, 3621642; 512570,
3621640; 512569, 3621637; 512568,
3621634; 512567, 3621632; 512565,
3621629; 512564, 3621626; 512563,
3621624; 512561, 3621621; 512560,
3621619; 512558, 3621616; 512557,
3621614; 512555, 3621611; 512554,
3621609; 512552, 3621607; 512550,
3621604; 512549, 3621602; 512547,
3621600; 512545, 3621597; 512543,
3621595; 512541, 3621593; 512539,
3621591; 512537, 3621589; 512535,
3621587; 512533, 3621585; 512531,
3621583; 512529, 3621581; 512527,
3621579; 512524, 3621577; 512522,
3621575; 512520, 3621573; 512518,
3621572; 512515, 3621570; 512513,
3621568; 512510, 3621567; 512508,
3621565; 512505, 3621564; 512503,
3621562; 512500, 3621561; 512498,
3621559; 512495, 3621558; 512493,
3621557; 512490, 3621556; 512487,
3621555; 512485, 3621553; 512482,
3621552; 512479, 3621551; 512476,
3621550; 512474, 3621550; 512471,
3621549; 512468, 3621548; 512465,
3621547; 512462, 3621546; 512460,
3621546; 512457, 3621545; 512454,
3621545; 512451, 3621544; 512448,
3621544; 512445, 3621543; 512442,
3621543; 512439, 3621543; 512437,
3621543; 512434, 3621543; 512431,
3621543; 512428, 3621542; 512425,
3621543; 512422, 3621543; 512419,
3621543; 512416, 3621543; 512413,
3621543; 512411, 3621543; 512408,
3621544; 512405, 3621544; 512402,
3621545; 512399, 3621545; 512396,
3621546; 512393, 3621546; 512391,
3621547; 512388, 3621548; 512385,
3621549; 512382, 3621550; 512379,
3621550; 512377, 3621551; 512374,
3621552; 512371, 3621553; 512369,
3621555; 512366, 3621556; 512363,
3621557; 512361, 3621558; 512358,
3621559; 512355, 3621561; 512353,
3621562; 512350, 3621564; 512348,
3621565; 512345, 3621567; 512343,
3621568; 512341, 3621570; 512338,
PO 00000
Frm 00042
Fmt 4701
Sfmt 4702
3621572; 512336, 3621573; 512334,
3621575; 512331, 3621577; 512329,
3621579; 512327, 3621581; 512325,
3621583; 512323, 3621585; 512321,
3621587; 512319, 3621589; 512317,
3621591; 512315, 3621593; 512313,
3621595; 512311, 3621597; 512309,
3621600; 512307, 3621602; 512305,
3621604; 512304, 3621607; 512302,
3621609; 512300, 3621611; 512299,
3621614; 512297, 3621616; 512296,
3621619; 512294, 3621621; 512293,
3621624; 512292, 3621626; 512290,
3621629; 512289, 3621632; 512288,
3621634; 512287, 3621637; 512286,
3621640; 512285, 3621642; 512284,
3621645; 512283, 3621648; 512282,
3621651; 512281, 3621653; 512280,
3621656; 512280, 3621659; 512279,
3621662; 512278, 3621665; 512278,
3621668; 512277, 3621670; 512277,
3621673; 512277, 3621676; 512276,
3621679; 512276, 3621682; 512276,
3621685; 512276, 3621688; 512275,
3621691; 512275, 3621694; 512275,
3621696; 512275, 3621699; 512276,
3621702; 512276, 3621705; 512276,
3621708; 512276, 3621711; 512277,
3621714; 512277, 3621717; 512277,
3621720; 512278, 3621722; 512278,
3621725; 512279, 3621728; 512280,
3621731; 512280, 3621734; 512281,
3621737; 512282, 3621739; 512283,
3621742; 512284, 3621745; 512285,
3621748; 512286, 3621750; 512287,
3621753; 512288, 3621756; 512289,
3621758; 512290, 3621761; 512292,
3621764; 512293, 3621766; 512294,
3621769; 512296, 3621771; 512297,
3621774; 512299, 3621776; 512300,
3621779; 512302, 3621781; 512304,
3621783; 512305, 3621786; 512307,
3621788; 512309, 3621790; 512311,
3621793; 512313, 3621795; 512315,
3621797; 512317, 3621799; 512319,
3621801; 512321, 3621803; 512323,
3621805; 512325, 3621807; 512327,
3621809; 512329, 3621811; 512331,
3621813; 512334, 3621815; 512336,
3621817; 512338, 3621818; 512341,
3621820; 512343, 3621822; 512345,
3621823; 512348, 3621825; 512350,
3621826; 512353, 3621828; 512355,
3621829; 512358, 3621831; 512361,
3621832; 512363, 3621833; 512366,
3621834; 512369, 3621835; 512371,
3621837; 512374, 3621838; 512377,
3621839; 512379, 3621840; 512382,
3621840; 512385, 3621841; 512388,
3621842; 512391, 3621843; 512393,
3621844; 512396, 3621844; 512399,
3621845; 512402, 3621845; 512405,
3621846; 512408, 3621846; 512411,
3621846; 512413, 3621847; 512416,
3621847; 512419, 3621847; 512422,
3621847; 512425, 3621847; 512428,
3621847; 512431, 3621847; 512434,
3621847; 512437, 3621847; 512439,
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3621847; 512442, 3621847; 512445,
3621846; 512448, 3621846; 512451,
3621846; 512454, 3621845; 512457,
3621845; 512460, 3621844; 512462,
3621844; 512465, 3621843; 512468,
3621842; 512471, 3621841; 512474,
3621840; 512476, 3621840; 512477,
3621839; 512480, 3621845; 512483,
3621854; 512485, 3621861; 512487,
3621867; 512490, 3621879; 512491,
3621887; 512491, 3621890; 512489,
3621902; 512489, 3621905; 512489,
3621907; 512490, 3621915; 512490,
3621918; 512488, 3621932; 512485,
3621940; 512479, 3621948; 512474,
3621953; 512470, 3621962; 512472,
3621980; 512473, 3621995; 512473,
3622014; 512473, 3622017; 512474,
3622021; 512475, 3622027; 512478,
3622038; 512479, 3622044; 512482,
3622052; 512486, 3622061; 512487,
3622065; 512492, 3622070; 512500,
3622081; 512503, 3622084; 512513,
3622088; 512528, 3622090; 512541,
3622094; 512559, 3622092; 512564,
3622092; 512566, 3622092; 512574,
3622091; 512586, 3622090; 512596,
3622088; 512606, 3622085; 512615,
3622076; 512626, 3622066; 512631,
3622057; 512633, 3622045; 512635,
3622031; 512637, 3622024; 512637,
3622013; 512636, 3622012; 512637,
3622004; 512637, 3621999; 512637,
3621994; 512636, 3621980; 512637,
3621969; 512639, 3621957; 512639,
3621947; 512634, 3621935; 512632,
3621926; 512629, 3621920; 512621,
3621909; 512618, 3621905; 512614,
3621896; 512609, 3621886; 512602,
3621879; 512598, 3621874; 512595,
VerDate Aug<31>2005
14:27 Mar 13, 2007
Jkt 211001
3621870; 512591, 3621863; 512582,
3621858; 512573, 3621849; 512568,
3621843; 512565, 3621839.
(iv) Subunit 4D. Land bounded by the
following UTM NAD27 coordinates
(E,N): 517545, 3617394; 517535,
3617393; 517529, 3617393; 517489,
3617395; 517485, 3617395; 517475,
3617396; 517466, 3617398; 517456,
3617400; 517446, 3617403; 517437,
3617407; 517428, 3617411; 517423,
3617414; 517362, 3617446; 517358,
3617448; 517350, 3617454; 517346,
3617457; 517290, 3617497; 517286,
3617499; 517279, 3617506; 517271,
3617513; 517265, 3617520; 517258,
3617528; 517257, 3617530; 517227,
3617570; 517223, 3617576; 517218,
3617584; 517213, 3617593; 517209,
3617602; 517205, 3617611; 517202,
3617621; 517200, 3617630; 517199,
3617637; 517192, 3617682; 517192,
3617685; 517191, 3617695; 517190,
3617705; 517190, 3617775; 517191,
3617785; 517192, 3617795; 517192,
3617799; 517204, 3617875; 517205,
3617881; 517208, 3617890; 517211,
3617900; 517214, 3617909; 517218,
3617918; 517220, 3617923; 517248,
3617975; 517251, 3617979; 517251,
3617979; 517252, 3617982; 517255,
3617988; 517259, 3617996; 517265,
3618005; 517270, 3618013; 517277,
3618021; 517284, 3618028; 517291,
3618035; 517299, 3618041; 517307,
3618047; 517315, 3618052; 517323,
3618057; 517361, 3618076; 517362,
3618076; 517371, 3618080; 517381,
3618084; 517390, 3618087; 517400,
3618089; 517405, 3618090; 517449,
3618097; 517453, 3618097; 517463,
PO 00000
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Fmt 4701
Sfmt 4702
11987
3618098; 517473, 3618099; 517477,
3618099; 517544, 3618097; 517550,
3618097; 517560, 3618096; 517570,
3618094; 517580, 3618092; 517581,
3618092; 517593, 3618088; 517599,
3618088; 517604, 3618087; 517614,
3618085; 517623, 3618083; 517633,
3618080; 517642, 3618077; 517651,
3618073; 517660, 3618068; 517668,
3618063; 517677, 3618057; 517684,
3618050; 517692, 3618044; 517712,
3618023; 517719, 3618016; 517726,
3618008; 517731, 3618000; 517737,
3617991; 517741, 3617982; 517745,
3617973; 517749, 3617964; 517752,
3617954; 517754, 3617945; 517755,
3617939; 517760, 3617906; 517761,
3617904; 517768, 3617858; 517768,
3617855; 517769, 3617846; 517774,
3617769; 517774, 3617769; 517774,
3617759; 517774, 3617688; 517774,
3617678; 517774, 3617674; 517769,
3617618; 517768, 3617613; 517766,
3617603; 517764, 3617593; 517761,
3617583; 517758, 3617574; 517756,
3617571; 517735, 3617524; 517733,
3617518; 517728, 3617509; 517723,
3617501; 517717, 3617493; 517711,
3617485; 517704, 3617478; 517696,
3617471; 517693, 3617468; 517663,
3617444; 517659, 3617440; 517651,
3617435; 517643, 3617429; 517635,
3617425; 517603, 3617409; 517603,
3617409; 517594, 3617405; 517584,
3617401; 517575, 3617399; 517565,
3617396; 517555, 3617395; 517545,
3617394.
(v) Note: Map of Unit 4, subunits 4A,
4B, 4C, and 4D (Map 5), follows:
BILLING CODE 4310–55–P
E:\FR\FM\14MRP2.SGM
14MRP2
*
*
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 / Proposed Rules
*
*
Dated: February 28, 2007.
David M. Verhey,
Acting Assistant Secretary for Fish and
Wildlife and Parks.
[FR Doc. 07–1100 Filed 3–13–07; 8:45 am]
*
BILLING CODE 4310–55–C
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14:27 Mar 13, 2007
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11988
Agencies
[Federal Register Volume 72, Number 49 (Wednesday, March 14, 2007)]
[Proposed Rules]
[Pages 11946-11988]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 07-1100]
[[Page 11945]]
-----------------------------------------------------------------------
Part II
Department of the Interior
-----------------------------------------------------------------------
Fish and Wildlife Service
-----------------------------------------------------------------------
50 CFR Part 17
Endangered and Threatened Wildlife and Plants; Designation of Critical
Habitat for Acanthomintha ilicifolia (San Diego thornmint); Proposed
Rule
Federal Register / Vol. 72, No. 49 / Wednesday, March 14, 2007 /
Proposed Rules
[[Page 11946]]
-----------------------------------------------------------------------
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
RIN 1018-AU86
Endangered and Threatened Wildlife and Plants; Designation of
Critical Habitat for Acanthomintha ilicifolia (San Diego thornmint)
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: We, the U.S. Fish and Wildlife Service (Service), propose to
designate critical habitat for Acanthomintha ilicifolia (San Diego
thornmint) under the Endangered Species Act of 1973, as amended (Act).
We have determined that a total of approximately 1,936 acres (ac) (783
hectares (ha)) in San Diego County, California, meets the definition of
critical habitat. We are proposing to exclude 1,302 ac (527 ha) from
the critical habitat designation. If these proposed exclusions are
adopted, this would result in a designation of critical habitat of
approximately 634 ac (257 ha) of land under Federal (553 ac (224 ha)),
and State and local (81 ac (33 ha)), ownership in San Diego County,
California.
DATES: We will accept comments from all interested parties until May
14, 2007. We must receive requests for public hearings, in writing, at
the address shown in the ADDRESSES section by April 30, 2007.
ADDRESSES: If you wish to comment on the proposed rule, you may submit
your comments and materials identified by RIN 1018-AU86, by any of the
following methods:
(1) You may send comments by electronic mail (e-mail) to
fw8cfwocomments@fws.gov. Include ``RIN 1018-AU86'' in the subject line.
(2) You may fax your comments to Jim Bartel, Field Supervisor,
Carlsbad Fish and Wildlife Office at 760-431-5901.
(3) You may mail or hand-deliver your written comments and
information to Jim Bartel, Field Supervisor, Carlsbad Fish and Wildlife
Office, 6010 Hidden Valley Road, Carlsbad, CA 92011.
(4) You may submit your comments at the Federal eRulemaking Portal,
https://www.regulations.gov. Follow the instructions for submitting
comments.
Comments and materials received, as well as supporting
documentation used in the preparation of this proposed rule, will be
available for public inspection, by appointment, during normal business
hours at the Carlsbad Fish and Wildlife Office at the above address
(telephone 760-431-9440).
FOR FURTHER INFORMATION CONTACT: Jim Bartel, Field Supervisor, Carlsbad
Fish and Wildlife Office at the address or telephone number listed
under ADDRESSES. Persons who use a telecommunications device for the
deaf (TDD) may call the Federal Information Relay Service (FIRS) at
800-877-8339.
SUPPLEMENTARY INFORMATION:
Public Comments Solicited
We intend that any final action resulting from this proposal 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 rule are hereby solicited. Comments
particularly are sought concerning:
(1) The reasons any habitat should or should not be determined to
be critical habitat as provided by section 4 of the Act, including
whether the benefit of designation will outweigh any threats to the
species due to designation;
(2) Specific information on the amount and distribution of
Acanthomintha ilicifolia habitat and what areas should be included in
the designation that were occupied at the time of listing that contain
the features essential for the conservation of the species, and why and
what areas that were not occupied at the time of listing are essential
to the conservation of the species;
(3) Land use designations and current or planned activities in the
subject areas and their possible impacts on proposed critical habitat;
(4) Our proposed exclusion of 1,302 acres (ac) (527 hectares (ha))
of non-Federal lands already conserved or targeted for conservation
within subarea plans under the San Diego Multiple Species Conservation
Program (MSCP) and the San Diego Multiple Habitat Conservation Program
(MHCP) from the final designation of critical habitat for Acanthomintha
ilicifolia under section 4(b)(2) of the Act. We are specifically
seeking public comment on our proposed exclusion of lands covered under
the City of Encinitas subarea plan of the MHCP (see Exclusions Under
Section 4(b)(2) of the Act for details of these HCPs). It is our
understanding that little progress has been made by the City of
Encinitas to finalize their subarea plan since the 2001 release of the
draft plan. Based on information received during the public comment
period, the Secretary may determine that sufficient progress has not
been made and that lands within the City of Encinitas' subarea plan
should not be excluded from the final designation. Specifically, useful
information would include: Whether essential lands within Encinitas are
being managed, or are proposed to be managed, to conserve A.
ilicifolia, and; the outlook for completion of the draft subarea plan.
Please provide information concerning whether the benefits of exclusion
of any of these specific areas outweigh the benefits of their inclusion
in designated critical habitat. If the Secretary determines the
benefits of including these lands outweigh the benefits of excluding
them, they will not be excluded from final critical habitat;
(5) Any foreseeable economic, national security, or other potential
impacts resulting from the proposed designation and, in particular, any
impacts on small entities; and
(6) Whether our approach to designating critical habitat could be
improved or modified in any way to provide for greater public
participation and understanding, or to assist us in accommodating
public concerns and comments.
If you wish to comment, you may submit your comments and materials
concerning this proposal by any one of several methods (see ADDRESSES).
Please submit e-mail comments to fw8cfwocomments@fws.gov. Please also
include ``Attn: RIN 1018-AU86'' in your e-mail subject line 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
message, contact us directly by calling our Carlsbad Fish and Wildlife
Office at phone number 760-431-9440. Please note that comments must be
received by the date specified in DATES in order to be considered.
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 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
[[Page 11947]]
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.
Role of Critical Habitat in Actual Practice of Administering and
Implementing the Act
Attention to and protection of habitat is paramount to successful
conservation actions. The role that designation of critical habitat
plays in protecting habitat of listed species, however, is often
misunderstood. As discussed in more detail below in the discussion of
exclusions under section 4(b)(2) of the Act, there are significant
limitations on the regulatory effect of designation under section
7(a)(2) of the Act. In brief, (1) designation provides additional
protection to habitat only where there is a Federal nexus; (2) the
protection is relevant only when, in the absence of designation,
destruction or adverse modification of the critical habitat would in
fact take place (in other words, other statutory or regulatory
protections, policies, or other factors relevant to agency decision-
making would not prevent the destruction or adverse modification); and
(3) designation of critical habitat triggers the prohibition of
destruction or adverse modification of that habitat, but it does not
require specific actions to restore or improve habitat.
Currently, only 483 species, or 37 percent of the 1,311 listed
species in the United States under the jurisdiction of the Service have
designated critical habitat. We address the habitat needs of listed
species through conservation mechanisms such as listing, section 7
consultations, the section 4 recovery planning process, the section 9
protective prohibitions of unauthorized take, section 6 funding to the
States, the section 10 incidental take permit process and cooperative,
nonregulatory efforts with private landowners. The Service believes
that it is these measures that may make the difference between
extinction and survival for many species.
In considering exclusions of areas proposed for designation, we
evaluate the benefits of designation in light of Gifford Pinchot Task
Force v. U.S. Fish and Wildlife Service, 378 F.3d 1059 (9th Cir. 2004)
(hereinafter Gifford Pinchot). In that case, the Ninth Circuit
invalidated the Service's regulation defining ``destruction or adverse
modification of critical habitat.'' In response, on December 9, 2004,
the Director issued guidance to be considered in making section 7
adverse modification determinations. This proposed critical habitat
designation does not use the invalidated regulation in our
consideration of the benefits of including areas in the proposed
designation. The Service will carefully manage future consultations
that analyze impacts to designated critical habitat, particularly those
that appear to be resulting in an adverse modification determination.
Such consultations will be reviewed by the Regional Office prior to
finalizing to ensure that an adequate analysis has been conducted that
is informed by the Director's guidance.
On the other hand, to the extent that designation of critical
habitat provides protection, that protection can come at significant
social and economic cost. In addition, the mere administrative process
of designation of critical habitat is expensive, time-consuming, and
controversial. The current statutory framework of critical habitat,
combined with past judicial interpretations of the statute, make
critical habitat the subject of excessive litigation. As a result,
critical habitat designations are driven by litigation and courts
rather than biology, and made at a time and under a timeframe that
limits our ability to obtain and evaluate the scientific and other
information required to make the designation most meaningful.
In light of these circumstances, the Service believes that
additional agency discretion would allow our focus to return to those
actions that provide the greatest benefit to the species most in need
of protection.
Procedural and Resource Difficulties in Designating Critical Habitat
We have been inundated with lawsuits for our failure to designate
critical habitat, and we face a growing number of lawsuits challenging
critical habitat determinations once they are made. These lawsuits have
subjected the Service to an ever-increasing series of court orders and
court-approved settlement agreements, compliance with which now
consumes nearly the entire listing program budget. This leaves the
Service with little ability to prioritize its activities to direct
scarce listing resources to the listing program actions with the most
biologically urgent species conservation needs.
The consequence of the critical habitat litigation activity is that
limited listing funds are used to defend active lawsuits, to respond to
Notices of Intent to sue relative to critical habitat, and to comply
with the growing number of adverse court orders. As a result, listing
petition responses, the Service's own proposals to list critically
imperiled species, and final listing determinations on existing
proposals are all significantly delayed.
The accelerated schedules of court-ordered designations have left
the Service with limited ability to provide for public participation or
to ensure a defect-free rulemaking process before making decisions on
listing and critical habitat proposals, due to the risks associated
with noncompliance with judicially imposed deadlines. This in turn
fosters a second round of litigation in which those who fear adverse
impacts from critical habitat designations challenge those
designations. The cycle of litigation appears endless, and is very
expensive, thus diverting resources from conservation actions that may
provide relatively more benefit to imperiled species.
The costs resulting from the designation include legal costs, the
cost of preparation and publication of the designation, the analysis of
the economic effects and the cost of requesting and responding to
public comment, and in some cases the costs of compliance with the
National Environmental Policy Act (NEPA) (42 U.S.C. 4321 et seq.).
These costs, which are not required for many other conservation
actions, directly reduce the funds available for direct and tangible
conservation actions.
Background
It is our intent to discuss only those topics directly relevant to
the designation of critical habitat in this proposed rule. For more
information on the biology and ecology of Acanthomintha ilicifolia,
please refer to the final rule listing the species as threatened
published in the Federal Register on October 13, 1998 (63 FR 54938).
This species has been listed by the State of California as endangered
since 1982.
Species Description and Life History
Acanthomintha ilicifolia (San Diego thornmint) is an annual member
of the mint family in the genus Acanthomintha. This plant ranges in
height from 2 to 6 inches (in) (5 to 15 centimeters (cm)) and has
white, two-lipped, tubular flowers with rose-colored markings on the
lower lip (Jokerst 1993, p. 713). Members of this genus have paired
leaves and several sharp spiny bracts (modified leaves) below whorled
flowers. Acanthomintha ilicifolia can be distinguished from other
members of the genus by its flower, which has hairless anthers and
style.
[[Page 11948]]
Distribution, Ecology, and Habitat
Acanthomintha ilicifolia usually occurs on heavy clay soils in open
areas surrounded by shrubby vegetation. These openings are generally
found within coastal sage scrub, chaparral and native grassland of
coastal San Diego County and south to San Telmo in northern Baja
California, Mexico (Beauchamp 1986, p. 175; Reiser 2001, pp. 3-5).
Acanthomintha ilicifolia is frequently associated with gabbro soils,
which are derived from igneous rock, and gray calcareous clays derived
from soft calcareous sandstone (Oberbauer and Vanderwier 1991, pp. 208-
209). This species is endemic to San Diego County, California, and
northwestern Baja California, Mexico, and grows on open clay lenses
described as friable, meaning that these soils have a loose, crumbly
texture.
In the final listing rule for Acanthomintha ilicifolia (63 FR
54938, October 13, 1998), 32 of 52 historic populations were presumed
to be extant (still in existence). In the listing rule we estimated
that the total number of individual plants in all remaining populations
was approximately 150,000 to 170,000 (63 FR 54938). Throughout this
proposed rule, occurrences of A. ilicifolia are referred to by their
element occurrence (EO) number. This is a code that is assigned to each
specific location of rare species that is cataloged in the California
Natural Diversity Database (CNDDB). Element occurrences do not
necessarily represent populations, but are used to represent areas
where a species is found. Element occurrences that are close together
may be part of the same population. Therefore, the number of element
occurrences does not represent the number of populations that exist for
this species. For the purpose of this proposed critical habitat
designation, we are assuming that element occurrences within one mile
(1.6 kilometers (km)) of each other and on habitat that is not
fragmented by roads or structures are part of the same population.
Through surveys associated with the development of Habitat
Conservation Plans (HCPs) and additional surveys on public and private
lands since the time of listing, additional populations of A.
ilicifolia have been discovered. We currently have data for a total of
88 element occurrences (or 64 populations) of which 54 element
occurrences (or 34 populations) are extant or presumed extant and 34
element occurrences (or 30 populations) are considered to be extirpated
(no longer in existence) or possibly extirpated. Specifically, we
consider 68 element occurrences to have been known at the time of
listing in 1998 (52 historic populations) and an additional 20 element
occurrences to have been discovered since the time of listing (12 new
populations). Detailed information about the new element occurrences is
available upon request from the Carlsbad Fish and Wildlife Office (see
ADDRESSES).
Previous Federal Actions
Acanthomintha ilicifolia was federally listed as threatened on
October 13, 1998 (63 FR 54938), and has been listed as endangered by
the State of California since 1982 (CDFG 2006, p.1). This species
currently does not have a recovery plan.
At the time this plant was federally listed, the Service compared
the benefits of designating critical habitat to the detrimental effects
(threats) of increased collection and vandalism and the potential for
private landowner misunderstandings about the effects of critical
habitat designation on private lands (63 FR 54938, pp. 54951-54953).
Additionally, we conflated the jeopardy standard with the standard for
destruction or adverse modification of critical habitat, stating that a
jeopardy finding would be equivalent to a finding of adverse
modification of critical habitat thereby resulting in identical section
7 findings. Based on these factors, the Service found that designation
of critical habitat for A. ilicifolia was not prudent.
On August 10, 2004, the Center for Biological Diversity and
California Native Plant Society challenged our failure to designate
critical habitat for this species as well as four other plant species
(Center for Biological Diversity v. Norton, C-04-3240 JL (N. D. Cal.)).
In settlement of the lawsuit, the Service agreed to withdraw our
previous not prudent finding and deliver a proposed determination of
critical habitat, if prudent, to the Federal Register on or before
February 28, 2007 and a final designation by February 28, 2008.
We have re-evaluated the prudency of designating critical habitat
for this species. Despite the potential threats to this species from
collection and vandalism and the continuing potential for private
landowner misunderstandings about the effects of critical habitat
designation on private land, we believe that designation of critical
habitat will benefit A. ilicifolia. As a result of the Gifford Pinchot
court ruling in 2004, we now recognize the jeopardy standard and the
standard for destruction or adverse modification of critical habitat
are separate and distinct. Additionally, we recognize critical habitat
designations may provide benefits to the recovery of a species.
Therefore, we now find designation of critical habitat for A.
ilicifolia to be prudent because designation of critical habitat has
the potential to provide greater protections to the species and its
habitat than the jeopardy standard under section 7(a)(2) of the Act.
Critical Habitat
Critical habitat is defined in section 3 of the Act as--(i) the
specific areas within the geographical area occupied by a species, at
the time it is listed in accordance with the Act, on which are found
those physical or biological features (I) essential to the conservation
of the species and (II) that may require special management
considerations or protection; and (ii) specific areas outside the
geographical area occupied by a species at the time it is listed, upon
a determination that such areas are essential for the conservation of
the species. Conservation, as defined under section 3 of the Act, means
to use and the use of all methods and procedures which are necessary to
bring any endangered species or threatened species to the point at
which the measures provided pursuant to the Act are no longer
necessary. Such methods and procedures include, but are not limited to,
all activities associated with scientific resources management such as
research, census, law enforcement, habitat acquisition and maintenance,
propagation, live trapping, and transplantation, and, in the
extraordinary case where population pressures within a given ecosystem
cannot be otherwise relieved, may include regulated taking.
Critical habitat receives protection under section 7 of the Act
through the prohibition against destruction or adverse modification of
critical habitat with regard to actions carried out, funded, or
authorized by a Federal agency. Section 7 of the Act requires
consultation on Federal actions that are likely to result in the
destruction or adverse modification of critical habitat. The
designation of critical habitat does not affect land ownership or
establish a refuge, wilderness, reserve, preserve, or other
conservation area. Such designation does not allow government or public
access to private lands. Section 7 of the Act is a purely protective
measure and does not require implementation of restoration, recovery,
or enhancement measures.
To be included in a critical habitat designation, the habitat
within the area occupied by the species must first have features that
are essential to the conservation of the species. Critical habitat
designations identify, to the
[[Page 11949]]
extent known using the best scientific data available, habitat areas
that provide essential life cycle needs of the species (i.e., areas on
which are found the primary constituent elements, as defined at 50 CFR
424.12(b)). Habitat within the geographic area occupied by the species
at the time of listing may be included in critical habitat only if the
essential features thereon may require special management
considerations or protection. Areas outside of the geographic area
occupied by the species at the time of listing may only be included in
critical habitat if they are essential for the conservation of the
species. Accordingly, when the best available scientific data do not
demonstrate that the conservation needs of the species require
additional areas, we will not designate critical habitat in areas
outside the geographical area occupied by the species at the time of
listing. An area currently occupied by the species but not known to be
occupied at the time of listing will likely, but not always, be
essential to the conservation of the species and, therefore, typically
included in the critical habitat designation.
The Service's Policy on Information Standards Under the Endangered
Species Act, published in the Federal Register on July 1, 1994 (59 FR
34271), and Section 515 of the Treasury and General Government
Appropriations Act for Fiscal Year 2001 (Pub. L. 106-554; H.R. 5658)
and the associated Information Quality Guidelines issued by the
Service, provide criteria, establish procedures, and provide guidance
to ensure that decisions made by the Service represent the best
scientific data available. They require Service biologists, to the
extent consistent with the Act and with the use of the best scientific
data available, to use primary and original sources of information as
the basis for recommendations to designate critical habitat. When
determining which areas are critical habitat, a primary source of
information is generally the listing package for the species.
Additional information sources include the recovery plan for the
species, articles in peer-reviewed journals, conservation plans
developed by States and counties, scientific status surveys and
studies, biological assessments, or other unpublished materials and
expert opinion or personal knowledge. All information is used in
accordance with the provisions of Section 515 of the Treasury and
General Government Appropriations Act for Fiscal Year 2001 (Pub. L.
106-554; H.R. 5658) and the associated Information Quality Guidelines
issued by the Service.
Section 4 of the Act requires that we designate critical habitat on
the basis of the best scientific data available. Habitat is often
dynamic, and species may move from one area to another over time.
Furthermore, we recognize that designation of critical habitat may not
include all of the habitat areas that may eventually be determined to
be necessary for the recovery of the species. For these reasons,
critical habitat designations do not signal that habitat outside the
designation is unimportant or may not be required for recovery.
Areas that support populations but are outside the critical habitat
designation will continue to be subject to conservation actions
implemented under section 7(a)(1) of the Act and to the regulatory
protections afforded by the section 7(a)(2) jeopardy standard, as
determined on the basis of the best available information at the time
of the action. Federally funded or permitted projects affecting listed
species outside their designated critical habitat areas may still
result in jeopardy findings in some cases. Similarly, critical habitat
designations made on the basis of the best available information at the
time of designation will not control the direction and substance of
future recovery plans, habitat conservation plans, or other species
conservation planning efforts if new information available to these
planning efforts calls for a different outcome.
Methods
As required by section 4(b)(2) of the Act, we used the best
scientific data available in determining areas that contain the
features that are essential to the conservation of Acanthomintha
ilicifolia. This includes information from the proposed listing rule
(60 FR 40549, August 9, 1995); final listing rule (63 FR 54938, October
13, 1998); data from research and survey observations published in
peer-reviewed articles; site visits and unpublished survey data;
regional Geographic Information System (GIS) layers including soil,
vegetation and species coverages from San Diego County and data
compiled in the California Natural Diversity Database (CNDDB). More
specifically, the information sources used for this proposal include:
(1) CNDDB element occurrence data (2005 and 2006); (2) Bauder and
McMillan (1994, pp. 1-87); (3) McMillan (2001, pp. 1-91); (4) herbarium
records from San Diego Natural History Museum, University of California
at Berkeley and Rancho Santa Ana Botanical Garden; (5) personal
communications with A. ilicifolia experts (Bauder 2006; Hanson 2006;
Kelly 2005; McMillan 2006; Sproul 2006; and Vinje 2006); (6) site
visits by Service biologists to several known element occurrences of A.
ilicifolia in 2005 and 2006; and (7) information provided by the
Cleveland National Forest of the U.S. Forest Service (Winter and Young
2005).
Primary Constituent Elements
In accordance with section 3(5)(A)(i) of the Act and regulations at
50 CFR 424.12, in determining which areas to propose as critical
habitat, we consider those areas occupied by the species at the time of
listing that contain physical or biological features (primary
constituent elements (PCEs)) that are essential to the conservation of
the species, and that may require special management considerations or
protection. These include, but are not limited to, space for individual
and population growth and for normal behavior; food, water, air, light,
minerals, or other nutritional or physiological requirements; cover or
shelter; sites for breeding, reproduction, and rearing of offspring,
germination, and seed dispersal; and habitats that are protected from
disturbance or are representative of the historic geographical and
ecological distributions of a species.
The specific primary constituent element required for Acanthomintha
ilicifolia is derived from the biological needs of A. ilicifolia as
described in the proposed and final listing rules (60 FR 40549; 63 FR
54938).
Space for Individual and Population Growth and Normal Behavior
Acanthomintha ilicifolia occurs on isolated patches of clay soils
derived from gabbro and soft calcareous sandstone substrates (Oberbauer
and Vanderwier 1991, pp. 208-209) (PCE). The soils derived from gabbro
substrates are red to dark brown clay soils, and those derived from
soft calcareous sandstone are gray, sometimes loamy, clay soils. These
patches of clay soils are called ``clay lenses,'' and in San Diego
County and northern Baja California, Mexico, clay lenses are known to
support a variety of narrow endemic (restricted to a specific
geographic area) plants. Clay lenses tend to have an open or
unpopulated look because many common species cannot tolerate living on
these clay soils. Clay lenses are typically devoid of woody, perennial
shrubs (PCE). It is believed shrubs have difficulty surviving on these
soils because in the rainy winter months these soils become saturated
[[Page 11950]]
with water and the large root systems of shrubs are not able to get
oxygen (Oberbauer and Vanderwier 1991, pp. 208-209). Also, as the soils
become saturated they expand and move, and when the soils dry they
contract and crack, making it difficult for shrubs to become
established. Likewise, relatively few common annual plant species
inhabit clay lenses due to the harsh conditions, and those plants that
are adapted to these conditions, in some cases, have become
differentiated from their common relatives. Due to the absence of most
common native vegetation from these clay lenses, the areas where A.
ilicifolia occurs appear as open areas in a matrix of coastal sage
scrub or chaparral (PCE).
Clay lenses are generally inhabited by a specific flora that
consist of forbs, native grasses, and geophytes (perennial plants
propagated by buds on underground bulbs, tubers, or corms such as
lilies, iris, and onions). Native plant species that characterize the
vegetation found with Acanthomintha ilicifolia on clay lenses include
Hesperevax sparsiflora var. sparsiflora (erect evax), Harpagonella
palmeri (Palmer's grappling-hook), Convolvulus simulans (bindweed),
Apiastrum angustifolium (mock parsley), and Microseris douglasii ssp.
platycarpha (small flowered microseris) (Bauder et al. 1994, pp. 9-10;
McMillan 2006, p. 1; Vinje 2006b, pp. 1-2).
In addition to the characteristics discussed above, the texture and
structure of the clay lenses are essential for supporting the seedling
establishment and growth of Acanthomintha ilicifolia. This soil
provides many small pockets where seeds from A. ilicifolia become
lodged as they fall from decomposing plants (Bauder and Sakrison 1999,
p. 28). The seeds then stay in the soils until the temperatures become
cooler in the winter months and the soil becomes saturated with the
winter rains (Bauder and Sakrison 1997, p. 28). The seedlings then
germinate and grow to mature plants. These plants do best when they are
not crowded or shaded by other plants (Bauder and Sakrison 1999, p.
12). The loose, crumbly texture of the soil provides the proper
substrate to hold the seed bank and allow for root growth (PCE).
Clay lenses generally form on gentle slopes. An analysis of 20
sites where Acanthomintha ilicifolia was observed found that the slopes
range from 0 to 25 degrees, with the majority of the sites having
slopes below 20 degrees (Bauder et al. 1994, pp. 10-11) (PCE). This
study also found that many thriving, natural populations were on slopes
that faced southeast, south, southwest, and west, although not all
sites fit this pattern (Bauder et al. 1994, pp. 10-11). Using GIS, we
found that the known populations of Acanthomintha ilicifolia range in
elevation from sea level to 3,000 ft (914 m). Acanthomintha ilicifolia
occurs on several soil types. These soils are mapped as Las Posas,
Olivenhain, Redding, Huerhuero, Altamont, Cieneba, and Linne (Bowman
1973, pp. 22-24, 38-40, 54-55, 61-64, 67-68, and 71-72) and are derived
from gabbro and soft calcareous sandstone substrates with a loose,
crumbly structure and deep fissures that provide space for population
and individual growth and substrate for seedling establishment.
Water and Hydrology
The loose, crumbly clay soils that support Acanthomintha ilicifolia
act like a sponge and are saturated by winter rains. The saturation of
these soils allows for seeds of A. ilicifolia to imbibe with water and
germinate in the cool winter months (Bauder and Sakrison 1997, p. 32).
As such, the species requires a natural hydrological regime to
reproduce. Since we do not have specific information on the
hydrological regime that this species requires, we did not include
hydrological regime as a primary constituent element.
Reproduction and Pollination
The breeding system of Acanthomintha ilicifolia has not been
studied, but it has been determined that other members of the genus
Acanthomintha are self-compatible (Steeck 1995, pp. 27-33). A 1996
study (Bauder and Sakrison 1997, p. 38) found that several insect
species visited the flowers and moved from plant to plant. These
insects represented possible pollinators of A. ilicifolia; however,
none were thought to represent species-specific pollinators (Bauder and
Sakrison 1997, p. 39). Since we do not have information on any species-
specific pollinators that visit A. ilicifolia, we did not include
pollinators as a primary constituent element.
Primary Constituent Elements for Acanthomintha ilicifolia
Pursuant to our regulations, we are required to identify the known
physical and biological features (PCEs) essential to the conservation
of Acanthomintha ilicifolia.
Based on our current knowledge of the life history, biology, and
ecology of the species and the requirements of the habitat to sustain
the essential life history functions of the species, we have determined
that the PCE for Acanthomintha ilicifolia is:
Clay lenses that provide substrate for seedling establishment and
space for growth and development of Acanthomintha ilicifolia, that are:
(a) Within chaparral and coastal sage scrub;
(b) On gentle slopes ranging from 0 to 25 degrees;
(c) Derived from gabbro and soft calcareous sandstone substrates
with a loose, crumbly structure and deep (approximately 2 feet (60 cm))
fissures; and
(d) Characterized by a low density of forbs and geophytes, and a
low density or absence of shrubs.
This proposed designation is designed for the conservation of those
areas containing the PCE necessary to support one or more of the
species' life history functions. All units and subunits in this
proposed designation contain the PCE and support multiple life
processes. This proposed rule would protect the PCE and thus the
conservation function of the habitat.
Criteria Used To Identify Critical Habitat
As required by section 4(b)(1)(A) of the Act, we use the best
scientific and commercial data available in determining areas that
contain the features that are essential to the conservation of
Acanthomintha ilicifolia. All of the areas proposed for designation are
currently occupied by the species. Occupied areas were determined from
survey data and element occurrence data in the CNDDB (CNDDB 2006). For
the purpose of this proposal, we assumed that each element occurrence
represents a population of A. ilicifolia, except in cases where there
are several element occurrences located within 1 mile (1.6 km) of each
other and the habitat is not fragmented by manmade features. In these
cases, we considered the group of element occurrences as a single
population. Examples of this include the Manchester Preserve in
Encinitas (element occurrence (EO) 28, EO 42, and EO 54), McGinty
Mountain near Jamul (EO 21, EO 22, and EO 30), and Viejas and Poser
Mountains near Alpine (EO 12, EO 50, EO 51, EO 62, EO 73, EO 74, and EO
75).
We then identified the areas that contain the features that are
essential to the conservation of A. ilicifolia by identifying areas
that: (1) Support populations that occur on rare or unique habitat
within the species' range; (2) support the largest known populations of
A. ilicifolia; or (3) support stable populations of A. ilicifolia.
These
[[Page 11951]]
criteria are explained in greater detail below. Areas containing the
primary constituent elements and that meet at least one of the above
criteria were considered for critical habitat designation. To evaluate
locations occupied by this species we used: the California Natural
Diversity Database (CNDDB 2006); a study by Bauder et al. (1994);
biological surveys (City of San Diego 2000; City of San Diego 2001;
City of San Diego 2003; City of San Diego 2004; City of San Diego 2005;
Conservation Biology Institute 2002, p. A3-1; County of San Diego 2002,
p. 17; Dudek and Associates, Inc. 2006, Appendix A pp. 3-4; Helix
Environmental Planning, Inc. 2002, p. 6; and REC Consultants, Inc.
2004, p. figure 5); and interviews with botanists working on this
species (Kelley 2005; McMillan 2006).
The first criterion we used to identify proposed critical habitat
was areas that support populations that occur on rare or unique habitat
within the species' range. The majority of areas that currently support
Acanthomintha ilicifolia are on dark brown to reddish brown clay soils
that are derived from gabbro substrates. Historically, A. ilicifolia
also occurred on gray clay soils that are derived from soft calcareous
sandstone substrates. The only remaining population on this soil type
is northeast of the intersection of Palomar Airport Road and El Camino
Real, in the City of Carlsbad. Conserving unique soil types that this
species occurs on will help to reduce the risk of extinction for this
species because it may allow for the preservation of a greater amount
of genetic diversity within the species' gene pool. Therefore, this
area containing population (EO 70) is proposed for critical habitat
designation under criterion one.
The second criterion we used to identify proposed critical habitat
was areas that support the largest known populations of Acanthomintha
ilicifolia. The CNDDB includes data for this species that date back to
1978. Populations of this species range from just a few individual
plants to several thousand. The majority of the known populations range
from 50 to 2,000 plants. Yet, there are four populations that stand out
as the largest, each having greater than 25,000 plants. The four
largest populations and the estimated population at each location are:
Sycamore Canyon (EO 32), 31,000 plants; Slaughterhouse Canyon (EO 64),
60,000 plants; Viejas and Poser Mountains (EO 12, EO 50, EO 51, EO 62,
EO 73, and EO 74), 29,650 plants; and Hollenbeck Canyon (EO L), 100,000
plants. These large populations are vital for the conservation of this
species because they occur within large blocks of open space and are
less likely to be impacted by edge effects associated with smaller
populations in highly urbanized areas. Additionally, the conservation
of these large populations will increase the persistence of the species
across its range. Therefore, the area containing these populations is
proposed for critical habitat designation under criterion two. These
four populations represent approximately 75 percent of the total known
plants of this species.
The third criterion we used to identify proposed critical habitat
was areas that support stable populations of Acanthomintha ilicifolia.
For the purpose of this proposed critical habitat designation, we
defined stable populations as those that contained more than 1,000
plants at least once during the period for which we have survey data.
We evaluated the population data from the CNDDB and determined that
populations with more than 1,000 plants at one time had the ability to
rebound following years with low population numbers. Therefore, we
considered populations with more than 1,000 plants to have a high
probability of persisting into the future and thus contribute to the
conservation of the species. The locations of these populations are
generally characterized by a series of clay lenses where the plants are
found in a matrix of intact coastal sage scrub and chaparral. Although
these areas are not free from exotic plant competitors, these
populations have persisted over time without being out-competed by the
exotic plant species present. This may be due in part to the low
density of exotic plant species at these locations. In addition to all
of the areas that meet criterion two, five other areas meet criterion
three: the southeast portion of the City of Carlsbad (EO 47); the
Manchester Preserve in Encinitas (EO 28, EO 42, and EO 54); Los
Pe[ntilde]asquitos Canyon (EO 19); Sabre Springs (EO 36); and McGinty
Mountain in the southern part of San Diego County (EO 21, EO 22, and EO
30). Each of these areas provides habitat that consistently supports
large populations of A. ilicifolia. Therefore, the area containing
these populations is proposed for critical habitat designation under
criterion three.
The 10 areas that we identified as meeting the criteria for
critical habitat contain the features that are essential for the
conservation of this species. These areas support the only population
of Acanthomintha ilicifolia on calcareous clay soil and the largest and
most stable populations. These areas were mapped using data from field
surveys and element occurrences in the CNDDB (CNDDB 2006), and unit
boundaries were created using GIS.
Annual plants experience annual fluctuation in population density
and spatial distribution. Through the review of existing survey data
and as a result of field work conducted by Service biologists, it
appears that this holds true for Acanthomintha ilicifolia, as
additional individuals are frequently located outside initially mapped
occurrence areas (Bauder et al. 2004, pp. 14-15; CNDDB 2006, pp. 11,
28-29, and 70; Service unpublished data 2006). Because soil data are
not available on a fine enough scale to ensure that proposed critical
habitat included all occupied habitat, each area mapped for A.
ilicifolia in the CNDDB was enlarged to include habitat within 500 ft
(152 m) around the edge of mapped occurrences. Using aerial
photography, we confirmed that no identifiable portion of an occupied
clay lens appeared to have been inadvertently omitted and removed
manmade features such as roads, buildings, parking lots and
agricultural fields. This boundary was then used as our proposed
critical habitat boundary.
When determining proposed critical habitat boundaries within this
proposed rule, we made every effort to avoid including developed areas
such as lands covered by buildings, paved areas, and other structures
that lack the PCE for Acanthomintha ilicifolia. The scale of the maps
prepared under the parameters for publication within the Code of
Federal Regulations may not reflect the exclusion of such developed
areas. Any such structures and the land under them inadvertently left
inside critical habitat boundaries shown on the maps of this proposed
rule have been excluded by text in the proposed rule and are not
proposed for designation as critical habitat. Therefore, Federal
actions limited to these areas would not trigger section 7
consultation, unless they may affect the species or primary constituent
elements in adjacent critical habitat.
We are proposing to designate critical habitat on lands that we
have determined were occupied at the time of listing that contain the
PCE that supports life history functions essential for the conservation
of the species and lands that were not known to be occupied at the time
of listing, but that we have determined are essential to the
conservation of the species. The lands that were not known to be
occupied at the time of listing are all currently occupied and contain
the PCE essential for the conservation of the species. The 10 areas
defined above, each representing one population, have been
[[Page 11952]]
categorized into four units. Due to large amounts of area that did not
contain the PCE in each of the four units, the units were further
broken down into 17 subunits so that the essential habitat could be
accurately mapped and not include areas that do not have the PCE. These
units/subunits are described in the Unit Descriptions section.
Section 10(a)(1)(B) of the Act authorizes us to issue permits for
the take of listed animal species incidental to otherwise lawful
activities. An incidental take permit application must be supported by
a habitat conservation plan (HCP) that identifies conservation measures
that the permittee agrees to implement for the species to minimize and
mitigate the impacts of the requested incidental take. We often exclude
non-Federal public lands and private lands that are covered by an
existing operative HCP and executed implementation agreement (IA) under
section 10(a)(1)(B) of the Act from designated critical habitat because
the benefits of exclusion outweigh the benefits of inclusion as
discussed in section 4(b)(2) of the Act. While section 10(a)(1)(B) of
the Act does not cover take of listed plant species, HCPs often cover
both listed animal and plant species. Acanthomintha ilicifolia is a
covered species in approved subarea plans under two major HCPs, the San
Diego Multiple Species Conservation Program (MSCP) and the San Diego
Habitat Conservation Program (MHCP). We are proposing to exclude areas
from the final designation of critical habitat where this species is
covered by one of these HCPs. See the Exclusions under Section 4(b)(2)
of the Act for a detailed discussion of these exclusions. We identify
the areas proposed for exclusion in the discussion of individual
critical habitat units below.
Special Management Considerations or Protection
When designating critical habitat, we assess whether the areas
determined to be occupied at the time of listing contain primary
constituent elements that may require special management considerations
or protection.
As stated in the final listing rule, threats to Acanthomintha
ilicifolia include trampling and grazing, the presence of exotic plant
species, off-road vehicles (ORVs), mining, and urbanization (63 FR
54938). Through our review of the existing data on A. ilicifolia, the
threats listed in the final listing rule continue to impact this
species and could impact the PCE as well. Building on the information
contained in the final listing rule, data on the effects of competition
from exotic plant species have been studied in greater detail (Bauder
and Sakrison 1999, pp. 6-19, 28-44) and attempts have been made to
manage this threat (Kelly 2002, pp. 1-3).
Urban development near Acanthomintha ilicifolia populations may
alter the habitat characteristics required by the species. The
destruction of habitat can change the slope and aspect of the site,
making it uninhabitable for A. ilicifolia (PCE). The close proximity of
development to populations of A. ilicifolia may affect other aspects of
the site. For example, increased water runoff from developments may
erode the clay lens and change the topography of the site (Bauder et
al. 1994, p. 23) (PCE).
The introduction of exotic plant species such as Centaurea
melitensis can drastically change the species present in, and eliminate
the open character of, the clay lens habitat (PCE). Centaurea
melitensis has been shown, in field and greenhouse experiments, to
negatively effect the biomass (growth) and seed production
(reproduction) of Acanthomintha ilicifolia (Bauder and Sakrison 1999,
p. 16). Populations of A. ilicifolia that are close to urbanized areas
or in areas that have been heavily grazed generally have a high density
of exotic plant species. In disturbed soils, C. melitensis is a common
weed. When this and other exotic plant species become established they
can out-compete A. ilicifolia for light, water, nutrients, and space.
A. ilicifolia often grows larger and at a higher density when
competition with exotic weeds is reduced (Bauder and Sakrison 1999, pp.
12-16; Vinje 2007, p. 10).
The final listing rule (63 FR 54938) discusses the impacts of ORV
activity and trampling. In recent years the impacts associated with the
use of mountain bikes has been observed to cause similar impacts (Vinje
2006a, p. 1). Trampling, ORV activity, and mountain bike use outside of
designated, maintained trails can compact the loose, crumbly soils
(PCE). The repeated travel over a trail or track degrades the habitat
of Acanthomintha ilicifolia in two ways: (1) by displacing soil; and
(2) by compacting soil and reducing the amount of water that can
percolate, thus reducing the plant's ability to establish roots.
Mining has been documented as a threat at two sites known to
support Acanthomintha ilicifolia (63 FR 54938; Bauder et al. 1994, p.
17). Mining can alter many aspects of A. ilicifolia habitat. Heavy
machinery can compact or remove clay lenses (PCE) or alter the slope of
an area (PCE). The grading of large areas adjacent to A. ilicifolia
habitat can make those areas vulnerable to invasion by exotic plant
species and lead to the subsequent crowding and shading of A.
ilicifolia habitat (PCE). All of these impacts may in turn lead to the
disruption of the growth and reproduction of A. ilicifolia .
Proposed Critical Habitat Designation
We are proposing a total of 1,936 ac (783 ha) in four units as
critical habitat for Acanthomintha ilicifolia . These four units are
further subdivided into 17 subunits. The critical habitat areas
described below constitute our best assessment at this time of areas
known to be occupied at the time of listing that contain the primary
constituent elements that may require special management considerations
or protection, and those additional areas that were not known to be
occupied at the time of listing (subunits 3E and 4D), but are essential
to the conservation of Acanthomintha ilicifolia . The four units
proposed for designation as critical habitat are: (1) Unit 1: Northern
San Diego County; (2) Unit 2: Central San Diego County; (3) Unit 3:
Viejas Mountain and Poser Mountain, San Diego County; and (4) Unit 4:
Southern San Diego County. We are proposing to exclude 1,302 ac (527
ha) under section 4(b)(2) of the Act from the final designation of
critical habitat. Table 1 identifies the occupancy status for each
subunit. Table 2 identifies the acreage and ownership of the areas
being proposed as critical habitat and the areas proposed for exclusion
from the final designation under section 4(b)(2) of the Act (see
Relationship of Critical Habitat to Habitat Conservation Plan Lands--
Exclusions Under Section 4(b)(2) of the Act below for a detailed
discussion).
[[Page 11953]]
Table 1.--Occupancy of Proposed Critical Habitat units for Acanthomintha ilicifolia
----------------------------------------------------------------------------------------------------------------
Known to be occupied
Critical habitat unit to the time of Occupied currently? Acres (hectares)
listing?
----------------------------------------------------------------------------------------------------------------
Unit 1: Northern San Diego County
1A. Palomar Airport (EO 70)...... Yes.................. Yes.................. 88 ac (36 ha)
1B. Southeast Carlsbad (EO 47)... Yes.................. Yes.................. 73 ac (29 ha)
1C. Manchester (EO 28, EO 42 and Yes.................. Yes.................. 92 ac (37 ha)
EO 54).
Unit 2: Central San Diego County
2A. Los Penasquitos Canyon (EO Yes.................. Yes.................. 63 ac (25 ha)
19).
2B. Sabre Springs (EO 36)........ Yes.................. Yes.................. 52 ac (22 ha)
2C. Sycamore Canyon (EO 32)...... Yes.................. Yes.................. 306 ac (124 ha)
2D. Slaughterhouse Canyon (EO 64) Yes.................. Yes.................. 77 ac (31 ha)
Unit 3: Viejas Mountain and Poser
Mountain 3A. Viejas Mountain (EO Yes.................. Yes.................. 33 ac (13 ha)
73).
3B. Viejas Mountain (EO 50)...... Yes.................. Yes.................. 208 ac (84 ha)
3C. Viejas Mountain (EO 51)...... Yes.................. Yes.................. 318 ac (128 ha)
3D. Viejas Mountain (EO 62)...... Yes.................. Yes.................. 82 ac (33 ha)
3E. Poser Mountain (EO 74)....... No................... Yes.................. 34 ac (14 ha)
3F. Poser Mountain (EO 12)....... Yes.................. Yes.................. 163 ac (66 ha)
Unit 4: Southern San Diego County
4A. McGinty Mountain (EO 21)..... Yes.................. Yes.................. 18 ac (7 ha)
4B. McGinty Mountain (EO 22)..... Yes.................. Yes.................. 220 ac (89 ha)
4C. McGinty Mountain (EO 30)..... Yes.................. Yes.................. 27 ac (11 ha)
4D. Hollenbeck Canyon (EO L)..... No................... Yes.................. 84 ac (34 ha)
------------------------------
Total*......................... ..................... ..................... 1,936 ac (783 ha)
----------------------------------------------------------------------------------------------------------------
* Some columns may not sum exactly due to rounding of values.
Table 2.--Proposed Critical Habitat for Acanthomintha Ilicifolia and the Areas Being Proposed for Exclusion From
the Final Critical Habitat Designation Under Section 4(b)(2) of the Act (acres (ac), hectares (ha), CNDDB
Element Occurrences (EO))
----------------------------------------------------------------------------------------------------------------
Area that meets Area being considered
Critical habitat unit Land ownership the definition of Area proposed as for exclusion from final
critical habitat critical habitat critical habitat*
----------------------------------------------------------------------------------------------------------------
Unit 1: Northern San Diego
County
1A. Palomar Airport (EO 70). Private.......... 7 ac (3 ha)...... 7 ac (3 ha)..... 7 ac (3 ha)
State/Local...... 81 ac (33 ha).... 81 ac (33 ha)... 0 ac (0 ha)
1B. Southeast Carlsbad (EO Private.......... 73 ac (29 ha).... 73 ac (29 ha)... 73 ac (29 ha)
47).
1C. Manchester (EO 28, EO 42 Private.......... 92 ac (37 ha).... 92 ac (37 ha)... 92 ac (37 ha)
and EO 54).
Unit 2: Central San Diego
County
2A. Los Penasquitos Canyon State/Local...... 63 ac (25 ha).... 63 ac (25 ha)... 63 ac (25 ha)
(EO 19).
2B. Sabre Springs (EO 36)... Private.......... 1 ac (1 ha)...... 1 ac (1 ha)..... 1 ac (1 ha)
State/Local...... 51 ac (21 ha).... 51 ac (21 ha)... 51 ac (21 ha)
2C. Sycamore Canyon (EO 32). Private.......... 30 ac (12 ha).... 30 ac (12 ha)... 30 ac (12 ha)
State/Local...... 276 ac (112 ha).. 276 ac (112 ha). 276 ac (112 ha)
2D. Slaughterhouse Canyon Private.......... 77 ac (31 ha).... 77 ac (31 ha)... 77 ac (31 ha)
(EO 64).
Unit 3: Viejas Mountain and
Poser Mountain
3A. Viejas Mountain (EO 73). Private.......... 33 ac (13 ha).... 33 ac (13 ha)... 33 ac (13 ha)
3B. Viejas Mountain (EO 50). Private.......... 156 ac (63 ha)... 156 ac (63 ha).. 156 ac (63 ha)
Federal.......... 52 ac (21 ha).... 52 ac (21 ha)... 0 ac (0 ha)
3C. Viejas Mountain (EO 51). Private.......... 38 ac (15 ha).... 38 ac (15 ha)... 38 ac (15 ha)
Federal.......... 280 ac (113 ha).. 280 ac (113 ha). 0 ac (0 ha)
3D. Viejas Mountain (EO 62). Private.......... 50 ac (20 ha).... 50 ac (20 ha)... 50 ac (20 ha)
Federal.......... 32 ac (13 ha).... 32 ac (13 ha)... 0 ac (0 ha)
3E. Poser Mountain (EO 74).. Federal.......... 34 ac (14 ha).... 34 ac (14 ha)... 0 ac (0 ha)
3F. Poser Mountain (EO 12).. Private.......... 7 ac (3 ha)...... 7 ac (3 ha)..... 7 ac (3 ha)
Federal.......... 156 ac (63 ha)... 156 ac (63 ha).. 0 ac (0 ha)
Unit 4: Southern San Diego
County
4A. McGinty Mountain (EO 21) Private.......... 18 ac (7 ha)..... 18 ac (7 ha).... 18 ac (7 ha)
4B. McGinty Mountain (EO 22) Private.......... 210 ac (85 ha)... 210 ac (85 ha).. 210 ac (85 ha)
State/Local...... 10 ac (4 ha)..... 10 ac (4 ha).... 10 ac (4 ha)
4C. McGinty Mountain (EO 30) Private.......... 27 ac (11 ha).... 27 ac (11 ha)... 27 ac (11 ha)
4D. Hollenbeck Canyon (EO L) Private.......... 23 ac (9 ha)..... 23 ac (9 ha).... 23 ac (9 ha)
State/Local...... 61 ac (25 ha).... 61 ac (25 ha)... 61 ac (25 ha)
---------------------------------------------------------------------------------
[[Page 11954]]
Total **.................. ................. 1,936 ac (783 ha) 1,936 ac (783 1,302 ac (527 ha)
ha).
----------------------------------------------------------------------------------------------------------------
* Lands proposed for exclusion from final critical habitat under section 4(b)(2) of the Act due to the
conservation provided for Acanthomintha ilicifolia from the City of Carlsbad and City of Encinitas subarea
plans of the San Diego MHCP and the City of San Diego and County of San Diego subarea plans of the San Diego
MSCP.
** Some columns may not sum exactly due to rounding of values.
Below, we present brief descriptions of all units and subunits, and
reasons why they meet the definition of critical habitat for
Acanthomintha ilicifolia. The PCE in each subunit of critical habitat
is threatened by the presence of exotic plants and recreational
activities (e.g., trampling, erosion and soil compaction caused by
hiking, off-road vehicle activity, and mountain biking); therefore,
special management considerations or protections of the PCE is required
to address these threats.
Unit Descriptions
Unit 1: Northern San Diego County
Unit 1 consists of 253 ac (102 ha) in northern San Diego County
divided into three subunits. This critical habitat unit includes
habitat for Acanthomintha ilicifolia in the cities of Carlsbad and
Encinitas under private, State, and local ownership (Table 1). The
majority of habitat for A. ilicifolia in northern San Diego County is
located in proximity to residential and commercial development;
however, the habitat being proposed as critical habitat is mostly on
land that has been set aside for the conservation of this and other
species. This unit contains five element occurrences, all of which were
known at the time of listing. The majority of the element occurrences
in this unit are covered by the San Diego Multiple Habitat Conservation
Program (MHCP). As part of the MHCP, each city will complete a subarea
plan. At this time, the City of Carlsbad has completed its subarea plan
under the San Diego MHCP and the City of Encinitas is nearing the
completion of its subarea plan. We are proposing to exclude 172 ac (70
ha) in the City of Carlsbad (portions of Subunit 1A and all of Subunit
1B) and the City of Encinitas (Subunit 1C) from the final designation
of critical habitat based on protections afforded to A. ilicifolia
under the Carlsbad and Encinitas subarea plans of the MHCP (see
Relationship of Critical Habitat to Habitat Conservation Plan Lands--
Exclusions Under Section 4(b)(2) of the Act below for more
information). The remaining 81 ac (33 ha) in Subunit 1A is owned by the
County of San Diego and is not part the San Diego MHCP.
Subunit 1A, Palomar Airport (EO 70)
Subunit 1A consists of 88 ac (36 ha) and was known to be occupied
at the time of listing. This subunit contains several habitat patches
known to support Acanthomintha ilicifolia and contains the feature
(PCE) considered to be essential to the conservation of the species.
The subunit meets our selection criteria because it supports a
population on a unique soil type (criterion 1). This is the only area
where A. ilicifolia is still known to occupy calcareous clay soils. The
PCE in this subunit may require special management considerations or
protection to control exotic plant species and reduce impacts
associated with recreational activities. This subunit is within the
designated preserve area for the Carlsbad subarea plan (referred to as
the Carlsbad Habitat Management Plan (HMP)) of the San Diego MHCP;
however, most of this subunit is owned by the County of San Diego and
not a part of the Carlsbad HMP. The portion covered by the Carlsbad HMP
will be managed for the conservation of this species. Therefore, we are
proposing to exclude the 7 ac (3 ha) of this subunit that are covered
by the Carlsbad HMP from the final designation of critical habitat
(Table 1) (see Relationship of Critical Habitat to Habitat Conservation
Plan Lands--Exclusions Under Section 4(b)(2) of the Act below for more
information). The remaining 81 ac (33 ha) of land owned by the County
of San Diego is proposed for inclusion in the designation of critical
habitat.
Subunit 1B, Southeast Carlsbad (EO 47)
Subunit 1B consists of 73 ac (29 ha), was known to be occupied at
the time of listing, and contains the feature (PCE) considered to be
essential to the conservation of the species. The subunit meets our
selection criteria because it supports a stable population (criterion
3). This population was estimated to have 400 plants in 1989, 2,000
plants in 1994, and 500 plants in 2006. The PCE in this subunit may
require special management considerations or protection to control
exotic plant species and reduce impacts associated with recreational
activities. The majority of the lands within this subunit are within an
area designated as a hardline conservation area (an area that has
already been or is slated to be preserved) and the entire subunit is
covered by the Carlsbad HMP of the San Diego MHCP which will provide
substantial protection and management of the PCE essential to the
conservation of Acanthomintha ilicifolia. Therefore, we are proposing
to exclude this subunit from the final designation of critical habitat
(Table 1) (see Relationship of Critical Habitat to Habitat Conservation
Plan Lands--Exclusions Under Section 4(b)(2) of the Act below for more
information).
Subunit 1C, Manchester (EO 42, EO 28, and EO 54)
Subunit 1C consists of 92 ac (37 ha), was known to be occupied at
the time of listing, and contains the feature (PCE) considered to be
essential to the con