Endangered and Threatened Wildlife and Plants; Designation of Critical Habitat for Brodiaea filifolia, 73820-73863 [05-23693]
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(telephone 760–431–9440; facsimile
760–431–9624).
SUPPLEMENTARY INFORMATION:
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
RIN 1018–AT75
Endangered and Threatened Wildlife
and Plants; Designation of Critical
Habitat for Brodiaea filifolia (threadleaved brodiaea)
Fish and Wildlife Service,
Interior.
ACTION: Final rule.
AGENCY:
SUMMARY: We, the Fish and Wildlife
Service (Service), are designating
critical habitat for the federally
threatened Brodiaea filifolia (threadleaved brodiaea) pursuant to the
Endangered Species Act of 1973, as
amended (Act). In total, approximately
597 acres (ac) (242 hectares (ha)) fall
within the boundaries of the critical
habitat designation. The critical habitat
is located in Los Angeles and San Diego
counties, California. Lands in Orange,
Riverside, and San Diego counties that
are covered by approved and draft
habitat conservation plans are excluded
under section 4(b)(2). Lands owned or
controlled by the Department of Defense
that are covered by an Integrated
Natural Resource Management Plan
(INRMP) that provides a benefit to the
species are exempt from critical habitat
under section 4(a)(3) of the Act. As a
result of revisions based on peer and
public comments and a re-evaluation of
methodology and mapping,
approximately 4,093 ac (1,656 ha) in Los
Angeles, San Bernardino, Orange, and
San Diego counties proposed as critical
habitat were removed or excluded from
this final designation. Lands designated
as critical habitat are under Federal and
private ownership. No Tribal lands are
included in this critical habitat
designation.
DATES: This rule becomes effective on
January 12, 2006.
ADDRESSES: Comments and materials
received, as well as supporting
documentation used in the preparation
of this final rule, are available for public
inspection, by appointment, during
normal business hours, at the Carlsbad
Fish and Wildlife Office, 6010 Hidden
Valley Road, Carlsbad, CA 92011
(telephone 760–431–9440). The final
rule, a list of references cited, the
economic analysis, and maps will also
be available on the Internet at https://
carlsbad.fws.gov.
FOR FURTHER INFORMATION CONTACT:
Field Supervisor, Carlsbad Fish and
Wildlife Office, at the above address
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Designation of Critical Habitat Provides
Little Additional Protection to Species
In 30 years of implementing the Act,
the Service has found that the
designation of statutory critical habitat
provides little additional protection to
most listed species, while consuming
significant amounts of available
conservation resources. The Service’s
present system for designating critical
habitat has evolved since its original
statutory prescription into a process that
provides little real conservation benefit,
is driven by litigation and the courts
rather than biology, limits our ability to
fully evaluate the science involved,
consumes enormous agency resources,
and imposes huge social and economic
costs. 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.
Role of Critical Habitat in Actual
Practice of Administering and
Implementing the Act
While attention to and protection of
habitat is paramount to successful
conservation actions, we have
consistently found that, in most
circumstances, the designation of
critical habitat is of little additional
value for most listed species, yet it
consumes large amounts of conservation
resources. Sidle (1987) stated, ‘‘Because
the Act can protect species with and
without critical habitat designation,
critical habitat designation may be
redundant to the other consultation
requirements of section 7.’’ Currently,
only 470 species or 37.5 percent of the
1,253 listed species in the U.S. under
the jurisdiction of the Service have
designated critical habitat.
We address the habitat needs of all
1,253 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, and the Section 10 incidental
take permit process. The Service
believes that it is these measures that
may make the difference for the
conservation of many species.
We note, however, that the August 6,
2004, Ninth Circuit judicial opinion,
Gifford Pinchot Task Force v. United
States Fish and Wildlife Service, found
our definition of adverse modification
was invalid. In response to the decision,
the Director has provided guidance to
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the Service based on the statutory
language. In this rule, our analysis of the
consequences and relative costs and
benefits of the critical habitat
designation is based on application of
the statute consistent with the Ninth
Circuit’s ruling and the Director’s
guidance.
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 the
limited listing funds are used to defend
active lawsuits, to respond to Notices of
Intent (NOIs) 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 almost no ability to
provide for adequate 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, is very
expensive, and in the final analysis
provides relatively little additional
protection to listed 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). None
of these costs result in any benefit to the
species that is not already afforded by
the protections of the Act enumerated
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earlier, and they directly reduce the
funds available for direct and tangible
conservation actions.
Background
By 1998, when the species was listed,
at least 25 percent of the known
Brodiaea filifolia populations or
occurrences had been eliminated by
urbanization and agricultural
conversion (63 FR 54975, October 13,
1998). Urban development continues to
be a threat to this species. Habitat for
the species is also threatened by off-road
vehicle use; non-agricultural grading
and disking for weed control; clearing
for firebreaks; alteration of existing
hydrologic conditions resulting from
construction and operation of flood
control structures; over-grazing; and
competition from non-native plant
species (USFWS 1998, RECON 1999,
CNDDB 2005). Occurrences of B. filifolia
in Orange County and some in San
Diego County are threatened by the
perennial Cynara cardunculus
(artichoke thistle or cardoon) (CNDDB
2005). B. filifolia and its habitat are also
threatened by dumping of manure and
sewage sludge on occupied habitat
along the San Jacinto River in western
Riverside County (Roberts in litt. 2005).
This material can alter the soil
chemistry and lead to changes in the
vegetation sustainable on the sites.
Previous Federal Actions
For more information on previous
Federal actions concerning Brodiaea
filifolia, refer to the final rule listing the
species as threatened, published in the
Federal Register on October 13, 1998
(63 FR 54975), and the proposed critical
habitat designation published in the
Federal Register on December 8, 2004
(69 FR 71284). A recovery plan for B.
filifolia has not yet been completed. The
following text discusses Federal actions
that occurred subsequent to the listing.
On November 15, 2001, a lawsuit was
filed against the Department of the
Interior (DOI) and the Service by the
Center for Biological Diversity and
California Native Plant Society,
challenging our ‘‘not prudent’’
determinations for eight plants,
including Brodiaea filifolia (Center for
Biological Diversity et al. v. Department
of the Interior et al., CV 01–2101). A
second lawsuit asserting the same
challenge was filed by the Building
Industry Legal Defense Foundation
(BILD) on November 21, 2001 (Building
Industry Legal Defense Foundation v.
Department of the Interior et al., CV 01–
2145). Both cases were consolidated on
March 19, 2002, and all parties agreed
to remand the critical habitat
determinations to the Service for
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additional consideration. On July 1,
2002, the U.S. District Court for the
Southern District of California directed
us to publish a new prudency
determination and, if prudent, propose
critical habitat for B. filifolia on or
before November 30, 2004, and to
publish a final rule on or before
November 30, 2005.
In the final listing rule, we
determined that critical habitat was not
prudent for Brodiaea filifolia because
such designation would provide no
benefit over that provided by listing on
private property where the species
occurs (63 FR 54975). The courts have
ruled that, in the absence of a finding
that the designation of critical habitat
would increase threats to a species, the
existence of another type of protection,
even if it offers potentially greater
protection to the species, does not
justify a ‘‘’not prudent’’’ finding
(Conservation Council for Hawaii v.
Babbitt 2 F. Supp. 2d 1280).
Accordingly, we withdrew our previous
determination that the designation of
critical habitat was not prudent for B.
filifolia and determined that critical
habitat designation for this species is
prudent. We had sufficient information
necessary to identify specific features
essential to the conservation of B.
filifolia and proposed critical habitat for
this species on December 8, 2004 (69 FR
71284). With the publication of this
rule, we are designating final critical
habitat for B. filifolia in compliance
with the court’s order.
Summary of Comments and
Recommendations
We contacted appropriate Federal,
State, and local agencies, scientific
organizations, and other interested
parties and invited them to comment on
the proposed critical habitat
designation. We also invited public
comment through the publication of
notices on December 17, 2004, in The
Press-Enterprise, Riverside, CA; San
Diego Union-Tribune, San Diego, CA;
Orange County Register, Santa Ana, CA;
and the Los Angeles Times, Los Angeles,
CA. The initial comment period ended
February 7, 2005. There were no
requests for public hearings.
During the comment period that
opened on December 8, 2004, and
closed on February 7, 2005, we received
19 comment letters directly addressing
the proposed critical habitat
designation: 4 comment letters were
received from 3 peer reviewers, 2 from
Federal agencies, and 13 from
organizations or individuals. We
received 2 additional comment letters
that were illegible. We attempted to
contact the authors of the letters but
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received no response; therefore, we
could not consider the information.
Thirteen commenters supported the
designation of critical habitat for
Brodiaea filifolia, and three opposed the
designation. Three letters included
comments or information, but did not
express support or opposition to the
proposed designation.
A second comment period to consider
the draft economic analysis of proposed
critical habitat for Brodiaea filifolia
opened on October 6, 2005, and closed
on October 20, 2005. During the
comment period we received 6 letters: 5
from organizations or individuals and 1
from a local government agency. In
opening the comment period on the
draft economic analysis, we also
reopened the comment period on our
critical habitat proposal. Comments
received during both comment periods
were grouped into general issue
categories relating to the proposed
designation or the draft economic
analysis.
Peer Review
In accordance with our joint policy
published on July 1, 1994 (59 FR
34270), we solicited review of our
proposed rule from at least three
appropriate independent specialists/
experts. The purpose of such review is
to ensure our final designation is based
on scientifically sound data,
assumptions, and analyses. We solicited
peer review from four knowledgeable
individuals with scientific expertise that
included familiarity with the species,
the geographic region in which the
species occurs, and conservation
biology principles. We received
responses from three of the peer
reviewers. The peer reviewers
supported the designation; however,
they expressed concern about errors and
omissions in the proposal, including the
exclusion of critical habitat on lands
covered by Habitat Conservation Plans
(HCP). Comments from peer reviewers
and other commenters are addressed in
the following summary, and corrections
and information are incorporated into
the final rule as appropriate.
Peer Reviewer Comments Related to
Previous Federal Actions, the Act, and
Implementing Regulations
Similar comments that were received
from other commenters are addressed in
this section to avoid redundancy.
(1) Comment: Two peer reviewers
requested that we provide a review of
the unique status of plants under the
Act, including the limited protection
plants are provided under section 9 of
the Act and the pros and cons of critical
habitat designation for plants. Another
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commenter indicated that Brodiaea
filifolia receives substantial protection
under the California Endangered
Species Act (CESA) and the California
Environmental Quality Act (CEQA) and
does not require special management
considerations or protection.
Our Response: Brodiaea filifolia is
listed as an endangered species under
the CESA. This allows the species to
receive greater attention during the land
use planning process by local
governments, public agencies, and
landowners. State listed plants are
protected from removal, except by
permit or agreement from the California
Department of Fish and Game (CDFG).
However, listing under the CESA
doesn’t remove all conservation threats
to the species. Areas that contain
features essential to the conservation of
B. filifolia and that may require special
management considerations or
protection would still warrant critical
habitat designation under the Act. The
benefits and limitations of critical
habitat designation for B. filifolia are
addressed in several different sections
throughout this document, including
the ‘‘Effects of Critical Habitat
Designation,’’ and ‘‘Application of
Section 3(5)(A), Exemption Under
Section 4(a)(3), and Exclusions Under
Section 4(b)(2) of the Act.’’
Peer Reviewer Comments Related to Life
History, Habitat Characteristics, and
Ecological Considerations
(2) Comment: Three peer reviewers
and five other commenters provided
additional information, clarifications,
and references for aspects of the biology,
associated vegetation, and soil
preferences of Brodiaea filifolia. One
peer reviewer considered ours an
excellent overview of the biology of the
species but lacking two references they
cited.
Our Response: We appreciate
additional information and clarification
and, where appropriate, we have
incorporated this into the final rule.
(3) Comment: One peer reviewer and
one individual stated that we should
have cited more recent information,
including the California Natural
Diversity Database (CNDDB), regarding
the historical range of Brodiaea filifolia,
pointing out that some new occurrences
have been discovered.
Our Response: In developing the
proposed rule we used data compiled
from the CNDDB database in 2003 as
well as an update in 2004 (CNDDB
2003; 2004). This is a running database
that includes periodic updates of
existing occurrence information and
new occurrence records. There was one
occurrence of Brodiaea filifolia
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identified in the 2004 update of the
CNDDB that we overlooked. This
occurrence is located in an
unincorporated area of central San
Diego County near Lake Hodges.
Fortunately, this occurrence of about
688 plants is being conserved under a
Minor Amendment to the San Diego
County MSCP.
Another occurrence in the same area
was not entered into the CNDDB until
April 6, 2005 (CNDDB 2005); therefore,
we were not able to consider it in the
proposed rule. It is not possible to
include an area in this final critical
habitat designation that was not
identified in the proposed rule. Because
we are under a court deadline to
complete this final rule, the publication
of a revised proposed rule to include
this area for public review and comment
could not have been completed in time
to comply with the court’s deadline.
(4) Comment: One peer reviewer cites
the dumping of sewage sludge as the
most serious threat to Brodiaea filifolia
along the San Jacinto River habitat in
Riverside County. The peer reviewer
also stated that these deposits alter the
soil chemistry.
Our Response: This comment is
appreciated and a discussion of this
threat has been incorporated into the
‘‘Background’’ section of this final rule.
(5) Comment: A peer reviewer and
two individuals provided differing
views on the issue of translocation. One
view asserted that translocation may not
have a high chance for success. The
other perspective considers it premature
to state that translocation is a threat to
the species. One peer reviewer
requested that we discuss all of the
translocated populations.
Our Response: We are uncertain about
the long-term viability of translocated
populations and their contribution to
the species as a whole, therefore, we did
not specifically include them in this
designation. However, translocated
populations may contribute to the longterm survival and recovery of the
species. Additional long-term
monitoring for genetic diversity and the
reproductive impact of these
populations is warranted. Only issues
specifically related to the critical habitat
designation are discussed in this final
rule, therefore, we have not included a
broad overview of translocated
populations in this document.
Peer Reviewer Comments Related to
Critical Habitat, Primary Constituent
Elements, and Methodology
(6) Comment: Two peer reviewers and
two other commenters expressed
concern about errors and lack of
attribution to citations in the proposed
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rule, suggesting that it be rewritten and
re-released. Several questions,
additions, and corrections to statements
and information relating to proposed
critical habitat units were provided by
peer reviewers and other commenters.
Our Response: Because of a court
deadline to complete this final rule, we
could not publish a revised proposed
rule for public review and comment in
time to comply with the court’s
deadline. One of the purposes of
releasing the proposed rule and draft
economic analysis for public review and
comment is to obtain substantive
information and materials related to the
proposed critical habitat designation.
We appreciate receiving additional
information, corrections, and
clarifications that were useful in our reevaluation of the proposed units and
unit descriptions. Where appropriate,
we have included this information and
answers to specific questions in the
final rule. See the ‘‘Summary of Changes
from Proposed Rule’’ section for a
review of changes in the final
designation.
(7) Comment: One peer reviewer
stated that we did not provide
information on our reasoning for
proposing critical habitat in a number of
locations in Riverside and San Diego
counties.
Our Response: We have re-evaluated
areas included in proposed critical
habitat. This final designation reflects
mapping refinements, our re-evaluation
of proposed areas under section 3(5)(A),
and exclusions under sections 4(a)(3)
and 4(b)(2) of the Act. Please refer to the
‘‘Criteria Used to Identify Critical
Habitat,’’ and the ‘‘Application of
Section 3(5)(A), Exemption Under
Section 4(a)(3) and Exclusions Under
Section 4(b)(2) of the Act’’ for more
information.
(8) Comment: Two peer reviewers
suggested literature citations, with one
requesting that we cite final versions
rather than draft documents, and the
other requesting that the references
cited list be published with the text of
the rule and posted on the Internet.
Our Response: Where appropriate, we
have incorporated these suggestions in
this rule. We cite the most current
version of documents available. As
stated in the ‘‘References Cited’’ section
of the rule, a list of references cited is
available upon request from the
Carlsbad Fish and Wildlife Office. We
will also make this list available on the
Internet at https://carlsbad.fws.gov.
(9) Comment: One peer reviewer and
a public commenter questioned our use
of a draft version of Bramlet and White
2004 (erroneously cited as White and
Bramlet 2004 in the proposed rule).
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Our Response: We referred to a
working table of occurrences (Table 3)
during the preparation of the proposed
rule. The information in this table was
considered to be one of the best
available on the occurrences of Brodiaea
filifolia. Only occurrences corroborated
from other sources are considered in
this final rule.
(10) Comment: Two peer reviewers
and two public commenters variously
stated that the section of the proposed
rule titled ‘‘Designation of Critical
Habitat Provides Little Additional
Benefit to Species’’ is generic,
editorializing, out of place in a proposal,
and political. One commenter wanted
us to point to the research that
specifically justifies this claim in
relation to Brodiaea filifolia.
Our Response: The section referenced
by the commenters is intended to be a
general statement regarding our position
on the designation of critical habitat. As
discussed in the preamble of this and
other critical habitat designation rules,
we believe that, in most cases,
conservation mechanisms provided
through section 7, 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 programs with
private and public landowners and
Tribes provide greater incentives and
conservation benefits than does the
designation of critical habitat.
(11) Comment: One peer reviewer and
one commenter requested a definition of
PCE. They also suggested clarifications
for PCEs relating to habitat descriptions,
soil types, slopes, and associated
vegetation types.
Our Response: As stated in the
‘‘Primary Constituent Elements’’ (PCE)
section of the proposed rule (69 FR
71284), PCEs are those physical or
biological features essential to the
conservation of a species, and that may
require special management
considerations or protection. The PCEs
for Brodiaea filifolia were based on the
best available information relating to the
species’ occurrences and its soil and
vegetation associations. Please refer to
the ‘‘Methods’’ section of this final rule
for a discussion of all information
sources used to define the PCEs for B.
filifolia.
(12) Comment: Two peer reviewers
noted the ability of Brodiaea filifolia to
persist on disturbed, degraded, or
disked sites and the suitability of these
sites if allowed to recover, especially by
natural flooding processes.
Our Response: It is likely that some
areas supporting occurrences of
Brodiaea filifolia have been degraded to
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some degree. The areas included in
proposed critical habitat and areas
excluded from proposed designation
under section 4(b)(2) of the Act were
identified as being occupied and
containing the physical or biological
features essential to the conservation of
the species. Lands included in this final
designation are occupied and contain
the features essential to the conservation
of B. filifolia. Please refer to the
‘‘Application of Section 3(5)(A),
Exemption Under 4(a)(3), and
Exclusions Under Section 4(b)(2) of the
Act’’ section for information about areas
removed, exempted, or excluded from
critical habitat.
(13) Comment: Two peer reviewers
and three other commenters provided
information and suggestions related to
the species’ biology, habitat description,
and condition, as well as boundaries of
the critical habitat subunits and areas
containing habitat with features
essential to the conservation of this
species that were excluded from critical
habitat in our proposal. One peer
reviewer also noted that some units
included unsuitable habitat. One
commenter recommended we change
the configuration of boundaries in the
Rancho Santalina/Loma Alta subunit to
better represent the areas containing
features essential to the conservation of
Brodiaea filifolia.
Our Response: We appreciate the
information and suggestions from these
commenters and, where appropriate, we
have incorporated the information on
subunit descriptions into this final rule.
Some of the commenters discussed
making the boundaries of critical habitat
subunits and areas containing habitat
with features essential to the
conservation of this species more
precise. We made such changes where
appropriate. We have attempted to map
the boundaries to exclude developed
land; however, we may not have been
able to exclude all developed land or
land that does not contain the PCEs.
Any such structures and the land under
them inadvertently left inside the
mapped critical habitat boundaries have
been excluded in the text portion of the
rule, and are not designated as critical
habitat. Federal actions limited to these
areas would not trigger section 7
consultations, unless they affect the
species and/or primary constituent
elements in adjacent critical habitat.
Some commenters suggested
including additional areas in the
proposed subunits or making boundary
adjustments in areas containing features
essential to the conservation of the
species that were excluded from
proposed designation. However, these
commenters did not provide sufficient
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site-specific data for us to adequately
evaluate their recommendations. We
reviewed the proposed Santalina/Loma
Alta subunit and determined it does not
meet the definition of critical habitat
under section 3(5)(A) of the Act. Please
refer to the section ‘‘Application of
Section 3(5)(A), Exemption Under
Section 4(a)(3), and Exclusions Under
Section 4(b)(2) of the Act’’ for more
information.
(14) Comment: Two peer reviewers
and one commenter questioned our use
of occurrences with 1,000 or more
plants as a measure of whether an area
contained habitat with features essential
to the conservation of Brodiaea filifolia.
One commenter questioned the science
behind our decision not to propose all
occurrences of B. filifolia in Orange and
San Diego counties as critical habitat.
Our Response: In developing our
proposal, we relied on several types of
information to determine whether an
occurrence of Brodiaea filifolia was
considered significant. As outlined in
the ‘‘Criteria Used to Identify Critical
Habitat’’ section, we evaluated
population estimates, soil types,
associated vegetation, and elevation. We
also evaluated the location of
occurrences in relation to the range of
the species. For example, occurrences
that supported less than 1,000 plants,
but which were on alkali playas were
considered to be significant. For an
explanation of why more areas in
Orange and San Diego counties were not
included in the final designation, please
refer to the ‘‘Application of Section
3(5)(A), Exemption Under Section
4(a)(3) and Exclusions Under Section
4(b)(2) of the Act’’ portion of this rule.
(15) Comment: One peer reviewer and
one individual questioned the value of
including small units (e.g., 6b (Mesa
Drive)), or those with few plants (e.g.,
subunits 4d (Prima Deschecha), 4f
(Talega/Segunda Deschecha), and 6a
(Alta Creek)) as critical habitat.
Our Response: We considered
occurrence information, soil types,
vegetation association and other factors
in our re-evaluation of proposed
subunits. As a result of our reevaluation, several proposed subunits,
including 4d, 4f, and 6a, were removed
from final designation. Subunit 6b
(Mesa Drive) is relatively small,
covering about 5 ac (2 ha), but it
supports a significant occurrence of
Brodiaea filifolia and contains features
essential to the conservation of the
species; therefore, it was included in
proposed critical habitat. However,
subunit 6b was excluded from final
designation under section 4(b)(2) of the
Act. Please see the ‘‘Summary of
Changes from Proposed Rule,’’ and
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‘‘Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the
Act’’ sections for more information.
(16) Comment: One peer reviewer
recommended that we add Domino or
Chino alkali soils to the description of
PCEs because Brodiaea filifolia occurs
on these soil types in Riverside County.
Our Response: We have reviewed this
information and have included these
soil types in our definition of the PCEs
for Brodiaea filifolia.
(17) Comment: Two peer reviewers
and one Federal agency commenter
questioned our inclusion of subunits 5a
(Miller Mountain) and 5b (Devil
Canyon) in proposed critical habitat
because most plants in subunit 5a and
some in subunit 5b are hybrids between
Brodiaea filifolia and Brodiaea orcuttii.
One peer reviewer noted that hybrids
occur in the City of San Marcos and on
Marine Corps Base, Camp Pendleton
(Camp Pendleton), although specific
numbers and locations were not
provided. One peer reviewer stated that
plants in areas containing features
essential to the conservation of the
species in Riverside County are prone to
hybridization. Another commenter,
knowledgeable about the genetics of
Brodiaea, stated that B. filifolia and B.
orcuttii form a unique line and could
hybridize only with each other.
Our Response: We acknowledge that
within subunits 5a and 5b, there are
substantial numbers of plants that are
hybrids of Brodiaea filifolia and
Brodiaea orcuttii (Boyd et al. 1992). The
population in subunit 5a is considered
to be largely hybridized and we cannot
determine that they can be considered
as contributors to the long-term
conservation of the species; therefore,
we removed this subunit from
consideration. Although plants in
subunit 5b also show some
hybridization, the extent of the
hybridization is less. The occurrence of
B. filifolia in subunit 5b is significant
and is found at one of the highest
elevations within the range of the
species. We have included the portion
of land in subunit 5b that is occupied
by B. filifolia and contains features
essential to the conservation of the
species in this final designation. Please
see the ‘‘Summary of Changes from
Proposed Rule’’ and ‘‘Application of
Section 3(5)(A), Exemption Under
Section 4(a)(3), and Exclusions Under
Section 4(b)(2) of the Act,’’ and ‘‘Unit
Descriptions’’ sections for more
information.
We are aware of a CNDDB (Element
Occurrence 10) report in the City of San
Marcos that included a reference to the
possible presence of hybrids between
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Brodiaea filifolia and B. jolonensis. This
area was identified as subunit 8d
(Upham) in our proposed rule. It has
been reported that putative hybrid
individuals of B. filifolia and another
species that has been erroneously
referred to B. jolonensis occur on the
site (Armstrong 2005). Though these
hybrid plants exhibit intermediate
characteristics between the two
theorized parental species, a third
species, B. orcuttii, also grows nearby
within the unit. According to Armstrong
(2005), the hybrid plants appeared to be
a ‘‘clonal population’’ restricted to ‘‘a
one acre area at the southwest end of the
property’’ and that these individuals
‘‘probably reproduced asexually through
cormlets.’’ Although Armstrong (2005)
found ‘‘numerous B. filifolia, B. orcuttii,
and (the material referred to as B.
jolonensis)’’ growing within the unit in
May 2005, he failed to observe any of
the hybrid plants. As a result, although
putative hybridization has been
reported for this unit, hybrid plants are
either no longer present or they
represent an undetectable, small
fraction of the overall population of B.
filifolia. The occurrence of B. filifolia in
this subunit is estimated to support
about 1,000 plants and contains features
essential to the conservation of the
species.
We were not able to confirm the
commenter’s reference to hybrids on
Camp Pendleton.
(18) Comment: One peer reviewer
considered the mapping of lands in
Riverside County that were excluded
from proposed critical habitat to be
inadequate. One individual requested
UTMs for these same areas.
Our Response: As stated in the
proposed rule, maps of the areas in
Riverside County containing features
essential to the conservation of Brodiaea
filifolia that were excluded under
section 4(b)(2) of the Act, based on
conservation measures outlined in the
Western Riverside County Multiple
Species Habitat Conservation Plan
(MSHCP), were available on our Web
site. We believe that the general public
finds these maps more useful than the
UTM coordinates. Also, GIS layers of
the areas proposed for critical habitat
designation as well as areas excluded
from proposed critical habitat are
available upon request from our office.
We will clarify the availability of this
information in future critical habitat
rules.
(19) Comment: One peer reviewer
expressed the importance of designating
critical habitat for Brodiaea filifolia in
irregularly flooded bottomland areas of
the San Jacinto River floodplain because
of concerns that alteration of the
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floodplain could adversely modify a
significant portion of the Riverside
County occurrences of the plant and
eliminate a unique element of the
species’ habitat associations (i.e., plants
adapted to alkali soils). The reviewer
stated that designation of critical habitat
in the San Jacinto River floodplain area
would strengthen the regulatory
effectiveness of section 7 by adding
‘‘adverse modification’’ to the jeopardy
standard available to the Service and
ensure that activities of the U.S. Army
Corps of Engineers (ACOE) do not
adversely modify the habitat. The
reviewer also indicated that thousands
of acres are undergoing alteration by
sewage sludge and manure dumping.
Our Response: We agree that areas
supporting Brodiaea filifolia in the San
Jacinto River floodplain are important
because they contain features essential
to the conservation of the species.
However, these areas have been
excluded from critical habitat because
the Western Riverside County MSHCP
addresses the conservation needs of the
species, including the maintenance of
floodplain processes along the San
Jacinto River. The Secretary has
determined the benefits of excluding
lands covered by the Western Riverside
County MSHCP outweigh the benefits of
including them in critical habitat (see
the ‘‘Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the
Act’’ section of this rule.)
(20) Comment: Two peer reviewers
and one individual commenter stated
that areas we identified as having
features essential to the conservation of
Brodiaea filifolia near the City of Corona
and in Moreno Valley in Riverside
County are erroneous and based on an
early draft of the Western Riverside
County MSHCP. The commenter
suggested they might be derived from
questionable biological surveys.
Our Response: We appreciate the
correction. After further evaluation, we
did not find reliable data validating the
occurrences of Brodiaea filifolia at these
locations, and we removed them from
consideration. For more information,
please refer to the ‘‘Summary of
Changes from Proposed Rule.’’
(21) Comment: One peer reviewer
suggested that we designate habitat
blocks that contain the entire San
Jacinto River floodplain to capture the
historical habitat of the species.
Our Response: When designating
critical habitat for Brodiaea filifolia we
identified land containing physical or
biological features essential to the
conservation of the species and which
may require special management
considerations or protection. Physical or
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biological features include areas needed
for pollen dispersal and pollination;
seed dispersal and germination, and
maintenance of seed banks; and areas
that provide the basic requirements for
growth. These features, referred to as
PCEs, are discussed in the ‘‘Primary
Constituent Elements’’ section of this
rule. Areas in western Riverside County,
including lands within the San Jacinto
River floodplain that are occupied by B.
filifolia and contain features essential to
the conservation of the species have
been excluded from critical habitat
pursuant to section 4(b)(2) of the Act
(see ‘‘Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the
Act.’’)
(22) Comment: One peer reviewer
questioned how land management of
reserves helps recovery of the species
with and without critical habitat.
Our Response: We are assuming the
peer reviewer is referring specifically to
reserves that are established in
conjunction with HCPs. Approved HCPs
include measures to monitor, minimize,
and mitigate impacts; and must provide
adequate funding. Management of
reserves in accordance with an HCP’s
issuance criteria would be carried our
regardless of a critical habitat
designation on identified reserve lands.
Only actions authorized, funded, or
carried out by a Federal agency that may
affect critical habitat would require
consultation with us and would not
affect actions undertaken on reserve
areas that do not have a Federal nexus.
Reserves established as part of an HCP
include monitoring and management to
ensure the areas retain their biological
value for the species.
Peer Review Comments Related to
Department of Defense (DoD) Lands
(23) Comment: One peer reviewer
requested a discussion of the
importance of populations of Brodiaea
filifolia on Camp Pendleton.
Our Response: Populations of
Brodiaea filifolia on Camp Pendleton
are of considerable importance not only
because of the numbers of plants
reported (over 4,000) from several
different occurrences, but also because
they are found in more than one
vegetation or soil association, including
grasslands and vernal pools; the
occurrences are distributed in a manner
that likely facilitates pollen transfer
among them and also with occurrences
to the north and south of Camp
Pendleton. Please see the ‘‘Application
of Section 3(5)(A), Exemption Under
Section 4(a)(3), and Exclusions Under
Section 4(b)(2) of the Act’’ for more
information about Camp Pendleton’s
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Integrated Natural Resource
Management Plan (INRMP) and other
measures Camp Pendleton is
undertaking to address B. filifolia on
their lands.
Peer Review Comments Related to the
NCCP/HCP Program, Section 7, and
Section 404
(24) Comment: Two peer reviewers
and one commenter disagreed with our
determination to exclude critical habitat
based on approved HCPs. One peer
reviewer expressed further concern that
it is uncertain whether HCPs will
protect these areas because no specific
preserve boundaries have been
proposed, relying instead on goals and
potential conservation. The reviewers
stated that we did not provide a clear
biological reason for excluding lands
covered by HCPs and questioned why
more areas were not determined to be
critical habitat.
Our Response: Under section 4(b)(2)
of the Act, the Secretary may exclude
any particular area from critical habitat
designation if the benefits of excluding
such area outweigh the benefits of
including it in critical habitat, unless it
is determined, based on the best
scientific and commercial data
available, that the failure to designate
such area as critical habitat will result
in the extinction of the species. We
evaluated the benefits of excluding
critical habitat on lands covered by
HCPs, including the Western Riverside
County MSHCP, the San Diego County
Multiple Habitat Conservation Plan
(MHCP) and its approved subarea plans,
the Orange County Central and Coastal
NCCP/HCP, and the Settlement
Agreement for Rancho Mission Viejo’s
Ranch Plan, a component of the draft
Orange County Southern Subregion
NCCP/HCP, against the benefits of
including such lands in critical habitat.
A major benefit of excluding these lands
from critical habitat is the facilitation of
continued partnerships with the various
signatory agencies, cities and
landowners involved with these NCCP/
HCP efforts. Although a possible benefit
of including these lands in critical
habitat would be to enhance education
about the species and its habitat needs,
we consider this benefit to have largely
been met through the public
participation process that occurred, and
continues to occur, during the
development and implementation of
these conservation planning efforts. We
acknowledge that the Western Riverside
County MSHCP does not describe a
hard-lined reserve, but it does identify
specific conservation goals and
objectives for Brodiaea filifolia,
including the conservation of 11
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occurrences in the two Core Areas in
western Riverside County where this
species is found.
Please refer to the ‘‘Application of
Section 3(5)(A), Exemption Under
Section 4(a)(3), and Exclusions Under
Section 4(b)(2) of the Act’’ section for
more discussion of the Western
Riverside County MSHCP and other
NCCP/HCP efforts.
(25) Comment: Two peer reviewers
state that the Lakeview/Nuevo Area
Plan (Dudek and Associates 2003) is
inconsistent with provisions of the
Western Riverside County MSHCP
because it has nearly the entire Criteria
Area zoned for residential development.
Our Response: Under the Western
Riverside County MSHCP, permittees
are obligated to adopt and maintain
ordinances or resolutions as necessary,
and amend their general plans as
appropriate, to implement the
requirements and fulfill the purposes of
the MSHCP and its associated
Implementing Agreement (IA) and
Permit (Dudek and Associates 2003).
(26) Comment: Two peer reviewers
requested that we discuss specific
conservation actions under the Western
Riverside County MSHCP that will
result in conservation of Brodiaea
filifolia. One reviewer specifically asked
what assurances are in place that
conservation benefits will occur before
Highway 79 is built through habitat for
the species.
Our Response: The Western Riverside
County MSHCP identifies specific goals
to be implemented for long-term
conservation of Brodiaea filifolia,
including conservation of at least 6,900
ac (2,760 ha) of habitat, containing 11
major locations supporting the species,
conducting surveys for B. filifolia in
certain areas, and maintaining
floodplain processes along the San
Jacinto River.
The assembly of the MSHCP
Conservation Area is anticipated to
occur over a period of time during the
life of the Permit. To ensure that the
resources ultimately conveyed to the
MSHCP Conservation Area are
maintained in their existing condition
prior to reserve assembly, the MSHCP
permittees are obligated to adopt and
maintain ordinances or resolutions and
to amend their general plans such that
they will be able to meet their
obligations under the MSHCP (Dudek
and Associates, Inc. 2003; 2003b).
Several covered activities discussed
under the MSHCP have the potential to
impact populations of Brodiaea filifolia
within the proposed MSHCP
Conservation Area, including the San
Jacinto River Flood Control Project and
the State Route 79 Realignment Project.
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These projects will require additional
consultation with our agency under
section 7 of the Act (Dudek and
Associates, Inc. 2003).
As a result of informal consultation
conducted to date on the State Route 79
Realignment Project, the City of Hemet
has adopted an Interim Urgency
Ordinance that preserves two avoidance
alternatives for the State Route 79
Realignment Project, both of which are
located outside of the MSHCP Criteria
Area, and also allows the City to ensure
that development efforts within the
MSHCP Criteria Area are coordinated
such that habitat conserved within the
Criteria Area does not become
fragmented, thereby allowing the City to
meet their obligations under the MSHCP
(City of Hemet 2005).
(27) Comment: One peer reviewer
stated that there was no protection of
land for Brodiaea filifolia before the
approval of the Western Riverside
County MSHCP, and there is no
protection now, as evidenced by the
ongoing dumping of sewage sludge and
manure on occupied habitat. The
reviewer cited an area along Case Road
where dumping has occurred.
Our Response: Permittees under the
Western Riverside County MSHCP are
obligated to adopt and maintain
ordinances or resolutions as necessary,
and amend their general plans as
appropriate, to implement the
requirements and to fulfill the purposes
of the MSHCP and its associated IA and
Permit (Dudek and Associates, Inc.
2003; 2003b). The Western Riverside
County MSHCP is a large, complex
habitat conservation plan, and its
implementation is expected to take
time. In its first year of implementation,
the Western Riverside County MSHCP
has already resulted in conservation and
management actions that address threats
to Brodiaea filifolia on private lands.
For example, the City of Hemet has
adopted an ordinance that has halted
the dumping of manure within the City
(City of Hemet 2002).
(28) Comment: One peer reviewer
expressed concern that there is no
assurance that prioritization of
conservation areas following the criteria
of the Western Riverside County
MSHCP will select the more favorable
biological areas over less favorable
areas. For example, while the Western
Riverside County MSHCP proposes one
method of conservation, another, yet to
be disclosed method, could prevail.
Our Response: We refer the reader to
our responses to comments 24 and 26
above and to the section titled
‘‘Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and
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Exclusions Under Section 4(b)(2) of the
Act’’ for more information.
(29) Comment: One peer reviewer,
citing the Fieldstone/La Costa
Associates HCP/Ongoing Multi-species
Plan (known as the Villages of La Costa
HCP), approved about 10 years ago,
states that HCPs are supposed to
provide for monitoring of the status of
covered species to measure the success
of conservation measures and asked us
to document the status of the reserve.
Our Response: Conservation
provisions for Brodiaea filifolia outlined
in the Villages of La Costa HCP include
protection of almost 6,000 plants in an
open-space preserve with long-term
management and monitoring, habitat
restoration, and control of invasive
plant species. Further information about
this HCP can be found in the section
titled ‘‘Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the
Act.’’
Public Comments Related to Life
History, Habitat Characteristics, and
Ecological Considerations
(30) Comment: One commenter
criticized our use of foraging distance
data based on Bombus taxa
(bumblebees), stating that their studies
had not recorded a single instance of
bumblebees visiting Brodiaea filifolia on
their property.
Our Response: We believe our use of
the 820 feet (ft) (250 meters (m))
distance for pollinator movement and
habitat is justified. Bell and Rey (1991)
noted Bombus californicus as one of the
native bees observed pollinating
Brodiaea filifolia on the Santa Rosa
Plateau in Riverside County. Please see
the ‘‘Criteria Used to Identify Critical
Habitat’’ section for a detailed
discussion.
(31) Comment: One commenter
criticized our omission of a study of
pollinators conducted by Rancho
Mission Viejo.
Our Response: The omission of this
report was inadvertent. The report
summarizes field studies conducted in
late spring 2003 and reports insects
visiting flowers of Brodiaea filifolia at
two locations and two times during the
season. Observations were made on
three dates between April and May
2003. Burrowing bees (Anthophoridae),
Sweat bees (Halictidae), and Flowerloving flies (Syrphidae) were the most
common groups of insects observed,
although it is not clear from the report
whether pollination by the various
insects was confirmed by observations
of fruit production by the plants.
Information from this report is
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incorporated, where appropriate, in this
final rule.
Public Comments Related to Critical
Habitat, Primary Constituent Elements,
and Methodology
(32) Comment: One commenter
suggested a method for designing the
size of conservation areas based on
Burgman et al. (2001).
Our Response: Although the
information is appreciated, it is
important to clarify the differences
between establishment of conservation
areas and the designation of critical
habitat. The designation of critical
habitat does not establish reserves,
preserves, wilderness areas, refuges or
other types of conservation areas. We
suggest readers refer to the sections on
‘‘Methods,’’ ‘‘Primary Constituent
Elements,’’ and ‘‘Effects of Critical
Habitat Designation’’ to more fully
understand how we identified areas for
critical habitat designation, the features
essential to the conservation of the
species, and the effect of critical habitat
on landowners.
(33) Comment: One commenter
wanted to know how many occurrences
in Riverside and San Diego counties are
outside designated critical habitat and
how this would affect the viability of
the species.
Our Response: A number of
occurrences in Riverside and San Diego
counties were not proposed for
designation because they were not
considered significant occurrences, or
were excluded from proposed critical
habitat under section 4(b)(2) of the Act.
Many of these areas receive
conservation consideration under
existing INRMPs, HCPs, or other
conservation instruments. Please refer to
the ‘‘Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the
Act’’ for more information. Please note
that, although habitat for Brodiaea
filifolia may be outside the boundaries
of designated critical habitat, it does not
mean these areas are unimportant or
may not be necessary for recovery of the
species.
(34) Comment: One commenter stated
that the purpose of critical habitat under
section 3 of the Act is to facilitate
recovery of species and that it should
include the opportunity for genetic
exchange, migration, and changes in
climate.
Our Response: The definition of
critical habitat has two prongs, that is,
one prong considers specific areas
within the geographic area occupied by
the species and the second prong
considers specific areas outside the
geographic area occupied by the species.
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To the extent that we can relate genetic
exchange, migration, and changes in
climate to physical and biological
features essential to the conservation of
the species and those areas also require
special management considerations or
protection (prong one) or based upon a
determination by the Secretary that an
unoccupied area is essential to the
conservation of the species (prong two),
we may and do consider those factors in
our designation of critical habitat.
Please see the ‘‘Designation of Critical
Habitat Provides Little Additional
Protection to Species’’ section and the
‘‘Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the
Act’’ for more information and
discussion.
(35) Comment: One commenter stated
there is a poor record of recovery for
species with critical habitat while
another commenter cited a report
indicating that species with critical
habitat are less likely to be in decline
and twice as likely to be recovering.
Our Response: The Service has been
unable to independently verify the
results of such studies. The fact that
there are conflicting studies shows that
the issue has not been settled. The
Service believes that most of the
protections of the Act come with listing
the species, and by far the most
successful recovery efforts come from
voluntary partnerships. Critical habitat
designation is not the sole means by
which conservation of a species may be
addressed.
(36) Comment: One commenter
characterized our proposed rule as a
sweeping designation that exceeds our
congressional mandate. The commenter
further stated that our designation
should be based on the estimated 825 ac
(334 ha) of land occupied by Brodiaea
filifolia identified in the final listing
rule (63 FR 54975). Another commenter
stated that Congress intended for critical
habitat to be extremely narrowly
defined and limited only to areas
necessary to bring the species to a point
where it is no longer in danger of
extinction.
Our Response: In developing the final
critical habitat designation for B.
filifolia, we reviewed all information
and data received during the two public
comment periods and have removed
from consideration those lands that do
not meet the criteria for designation.
Specific areas included in this final
designation contain the physical or
biological features essential to the
conservation of B. filifolia, including
space for pollen dispersal and
pollination; seed dispersal and
germination, and maintenance of seed
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banks; and areas that provide the basic
requirements for growth. Please refer to
the ‘‘Summary of Changes From
Proposed Rule,’’ and ‘‘Application of
Section 3(5)(A), Exemption Under
Section 4(a)(3), and Exclusions Under
Section 4(b)(2) of the Act’’ sections of
this rule for more information.
(37) Comment: One commenter
requested that we indicate which
parcels within critical habitat units/
subunits contain the PCEs. The
commenter also stated that all lands
within proposed units/subunits may not
contain all of the PCEs.
Our Response: In re-evaluating areas
proposed as critical habitat for Brodiaea
filifolia, we determined that some areas
do not contain features essential to the
conservation of the plant, and therefore
were removed from final designation.
The ‘‘Summary of Changes from
Proposed Rule’’ and ‘‘Application of
Section 3(5)(A), Exemption Under
Section 4(a)(3), and Exclusions Under
Section 4(b)(2) of the Act’’ sections
provide information about areas
removed from final designation. Due to
the scale at which we map critical
habitat boundaries, we do not include
parcel level detail. If lands within the
boundaries of critical habitat units/
subunits do not contain any PCEs, then
they have been excluded from the
designation in the text portion of the
rule.
(38) Comment: One commenter stated
that it was not good science to
‘‘extrapolate’’ genetic information from
studies on a ‘‘ubiquitous genera’’ such
as Lasthenia (lasthenia) to narrow
endemic species such as Brodiaea
filifolia.
Our Response: We cited the reference
to Lasthenia to highlight the
significance of outlying portions of a
species’ range to its genetic diversity.
Ornduff (1966) cites several species of
Lasthenia with morphological or
cytological variants at the margins of
their distributions. One example used
was Lasthenia fremontii, restricted to
vernal pools or wet meadows in the
Central Valley. This example was cited
for the purposes of explaining how
peripheral populations of Brodiaea
filifolia may be important to
maintaining the genetic diversity of the
taxa.
(39) Comment: Two commenters
questioned our 820 ft (250 m) pollinator
movement and habitat area. One
commenter thought it was too narrow,
the other thought it was too wide. One
cited a reference that one group of bees
(halictids) forage no more than 328 ft
(100 m).
Our Response: We have included
additional references and discussion in
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the ‘‘Background’’ section of this rule to
support our use of 820 ft (250 m) for a
pollinator movement and habitat area.
Please see the ‘‘Background’’ and
‘‘Criteria Used to Identify Critical
Habitat’’ sections for a detailed
discussion.
Public Comments Related to
Department of Defense Lands
(40) Comment: One Federal agency
commenter agreed with our exclusion of
mission-critical areas on Camp
Pendleton from critical habitat
designation under section 4(b)(2) of the
Act; however, they strongly disagreed
with our determination in the proposed
rule that Camp Pendleton’s Integrated
Natural Resource Management Plan
(INRMP) does not provide a benefit for
Brodiaea filifolia. The commenter
characterized critical habitat as
encroachment that would unacceptably
degrade Camp Pendleton’s mission. The
commenter also provided information
about programs and activities carried
out under the INRMP for B. filifolia.
Our Response: We appreciate the
information from the commenter and
have reviewed Camp Pendleton’s
INRMP, completed in November 2001
(U.S. Marine Corps 2001). Based on our
review of the INRMP and information
provided by the commenter, we
determined that the INRMP provides a
benefit for Brodiaea filifolia and have
exempted Camp Pendleton from critical
habitat designation pursuant to section
4(a)(3) of the Act. We have also
determined that exclusion of Camp
Pendleton pursuant to section 4(b)(2) of
the Act is also appropriate. Please see
the ‘‘Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the
Act’’ section for more information.
(41) Comment: One commenter
claimed we are inconsistent in
excluding Camp Pendleton from critical
habitat designation while other military
installations have critical habitat on
their lands.
Our Response: The commenter did
not cite which military installation(s)
had critical habitat designation(s);
therefore, we cannot provide specific
information about a particular
installation. Under section 4(b)(2) of the
Act, the Secretary shall designate
critical habitat, and revise critical
habitat on the basis of the best scientific
data available and after taking into
consideration the economic impact,
national security impact, and any other
relevant impact of specifying a
particular area as critical habitat. The
Secretary may exclude any particular
area from critical habitat if the benefits
of such exclusion outweigh the benefits
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of specifying such area as critical
habitat, unless the failure to designate
such area as critical habitat will result
in the extinction of the species. These
determinations are made by the
Secretary on a species-by-species and
area-by-area basis.
Section 318 of the fiscal year 2004
National Defense Authorization Act
(Pub. L. 108–136) amended the Act by
adding a new section 4(a)(3)(B). This
provision prohibits designation of
critical habitat on any lands or other
geographical areas owned or controlled
by the Department of Defense (DoD), or
designated for its use, that are subject to
an INRMP prepared under section 101
of the Sikes Act (16 U.S.C. 670a), if the
Secretary determines in writing that
such plan provides a benefit to the
species for which critical habitat is
proposed for designation.
The provisions of section 3(5)(A),
4(a)(3), and 4(b)(2) of the Act are fully
considered by us when designating
critical habitat. In some cases, critical
habitat may have been designated on
lands owned or controlled by the DOD
prior to the 2004 amendments to the
Act, or if otherwise determined to be
appropriate. Please see the section
‘‘Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the
Act’’ for more information. Any
revisions to designated critical habitat
could be considered through the formal
rulemaking process, subject to funding
availability.
Public Comments Related to NCCP/HCP
Program, Section 7, and Section 404
(42) Comment: One commenter stated
that the Ranch Plan, a component of the
draft Orange County Southern
Subregion NCCP/HCP is designed to
maximize gene flow for Brodiaea
filifolia and that implementation of the
Ranch Plan would not significantly
reduce genetic exchange because of
preexisting isolation. The commenter
requested their property be excluded
from critical habitat designation for B.
filifolia because of the protections
afforded the species under the draft
NCCP/HCP.
Our Response: In general, it is our
policy to consider excluding from
critical habitat designation HCPs that
are approved or are very close to
completion as indicated by the fact that
an Environmental Impact Statement/
Environmental Impact Report (EIS/EIR)
has already been prepared and released
for public review and comment. We
have not yet released a draft EIS/EIR for
the Orange County Southern Subregion
NCCP/HCP for public review and
comment; however, we are excluding
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from final critical habitat designation
the portion of lands within the
boundary of the draft NCCP/HCP that
are owned by Rancho Mission Viejo and
identified in the Ranch Plan under
section 4(b)(2) of the Act, based on a
recent Settlement Agreement. Please
refer to the section ‘‘Application of
Section 3(5)(A), Exemption Under
Section 4(a)(3), and Exclusions Under
Section 4(b)(2) of the Act’’ for more
information.
(43) Comment: One commenter stated
that the City of San Marcos does not
have an approved HCP and is not likely
to have one in the near future that
would warrant exclusion of their lands
from critical habitat under section
4(b)(2) of the Act.
Our Response: We did not exclude
any lands within the City of San Marcos
under section 4(b)(2) of the Act;
however, some lands in the City of San
Marcos were removed from further
consideration as critical habitat. Please
refer to the ‘‘Application of Section
3(5)(A), Exemption Under Section
4(a)(3), and Exclusions Under Section
4(b)(2) of the Act’’ for more information.
(44) Comment: Three commenters
supported our practice of excluding
critical habitat on areas covered by
HCPs. One also suggested that we
exclude areas covered under proposed
HCPs, noting that failure to do so would
remove incentives for them to
participate in these planning efforts.
This commenter also stated that
exemptions from critical habitat should
automatically follow approval of an
HCP. Another commenter further stated
that designating critical habitat in areas
covered by an HCP would impose
economic burdens, invite legal
challenges, and be a disincentive to
developing HCPs.
Our Response: It is our policy to
exclude from critical habitat lands
containing features essential to the
conservation of a federally listed species
that are covered by approved HCPs.
Pursuant to section 4(b)(2) of the Act,
critical habitat is to be designated or
revised based on the best scientific data
available and 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 any area from
critical habitat if the benefits of
excluding such area outweigh the
benefits of including it in critical
habitat, unless such exclusion will
result in the extinction of the species.
As part of the process of balancing the
benefits of including or excluding any
particular area as critical habitat,
including lands covered by approved
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HCPs and/or NCCP/HCPs, many factors
are considered, including the issues
identified by the commenters.
We make a determination to exclude
lands within the boundaries of draft
HCPs on a case-by-case basis. Generally,
we exclude critical habitat from lands
within the boundaries of draft HCPs or
NCCP/HCPs if we can point to
significant progress in the development
of a draft HCP and/or NCCP/HCP,
including the release of an EIR/EIS for
public review and comment or
development of some other identified
conservation commitment, and we are
confident the planning effort will lead
to a successful outcome. With regard to
automatic exemptions following
approval of HCPs or NCCP/HCPs,
section 4(b)(5)(A) of the Act requires
that any proposed regulation, including
revisions to critical habitat, be
published in the Federal Register and
that the public be afforded an
opportunity to review and comment.
Revisions to critical habitat designations
without providing notice to the public
would violate the Act. Please refer to the
section ‘‘Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the
Act’’ for more discussion of this topic.
(45) Comment: Two commenters
supported the designation of critical
habitat in areas with HCPs, one noting
that local agencies would welcome
assistance from the Service and the
other stating that critical habitat would
ensure that an HCP would meet its
success criteria.
Our Response: Both HCPs and critical
habitat designations are designed to
provide conservation measures to
protect species and their habitats. The
advantage of seeking new conservation
partnerships (through HCPs or other
means) is that they can offer active
management and other conservation
measures for the habitat on a full-time
and predictable basis. Critical habitat
requires Federal agencies that authorize,
fund or carry out activities that may
affect critical habitat to consult with us
to ensure such actions do not destroy or
adversely modify designated critical
habitat. In some cases, the designation
of critical habitat may remove
incentives to participate in the HCP
process because of added regulatory
uncertainty; increased costs to plan
development and implementation;
weakened stakeholder support; delayed
approval and development of an HCP;
and greater vulnerability to legal
challenge or other concerns. In some
instances, we have received direct
statements from landowners expressing
their intent to withdraw from other
types of cooperative efforts beneficial to
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the conservation of listed species if their
property was proposed for inclusion in
critical habitat. We work with HCP
applicants to ensure that their plans
meet the issuance criteria and that the
designation of critical habitat on lands
where an HCP is in development does
not delay the approval and
implementation of the HCP.
Additionally, HCPs include
conservation actions for covered species
whether or not the area is designated as
critical habitat.
(46) Comment: One commenter
wanted to know how we determined
that the benefits of excluding HCP areas
from critical habitat outweigh the
benefits of their inclusion.
Our Response: We refer the reader to
the ‘‘Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the
Act’’ section for an explanation of how
we have weighed the benefits of
including or excluding critical habitat
for Brodiaea filifolia on lands covered
by HCPs.
Comments Related to Economic
Analysis; and Other Relevant Impacts
(47) Comment: Two commenters
criticized our failure to include the
economic analysis with the critical
habitat proposal and one of these
commenters also noted the lack of an
EIS and National Environmental Policy
Act (NEPA) analysis.
Our Response: We published our
proposed designation of critical habitat
for Brodiaea filifolia in the Federal
Register on December 8, 2004 (69 FR
71284). At that time, our Division of
Economics and their consultants
initiated preparation of a draft economic
analysis of the proposed designation.
The draft economic analysis was
released for public review and comment
on October 6, 2005 (70 FR 58361), and
we accepted comments on both the draft
economic analysis and proposed rule
until October 20, 2005. With regard to
the preparation of an EIS and NEPA
analysis, it is our position that, outside
the Tenth Circuit, we do not need to
prepare environmental analyses as
defined by the NEPA in connection with
designating critical habitat. Please see
the ‘‘National Environmental Policy
Act’’ section of this rule for additional
information.
(48) Comment: One public commenter
stated that we failed to assess the impact
of multiple critical habitat designations
on landowners.
Our Response: To comply with the
10th Circuit Court of Appeal’s ruling in
the New Mexico Cattle Growers
Association case (248 F.3d at 1285) to
include all co-extensive effects, the
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economic analysis considers the
potential economic impacts of efforts to
protect the Brodiaea filifolia and its
habitat in critical habitat. It does so by
taking into account the cost of
conservation related measures that are
likely to be associated with future
economic activities that may adversely
affect the habitat within the proposed
boundaries. Our economic analysis fully
evaluated the economic and other
impacts of designating critical habitat
pursuant to section 4(b)(2) of the Act.
The economic and other impacts of
critical habitat are individually
analyzed in our economic analysis
report, which parallels our review of a
Federal action under section 7(a)(2) of
the Act. Our analysis of the effects of a
Federal action under section 7(a)(2) of
the Act would consider the effects to
any designated critical habitat. In the
proposed and final rules, we describe
and evaluate potential activities that
may adversely modify critical habitat or
may be affected by such designation
pursuant to section 4(b)(8) of the Act.
Each critical habitat designation may be
affected differently by a proposed action
in a manner that reflects the specific
physical and biological features that are
considered essential for the listed
species. Thus, our economic analysis
would reflect the economic and other
impacts specific to each designation.
(49) Comment: One commenter states
that the draft economic analysis (DEA)
is inconsistent with previous economic
analyses for Atriplex coronata var.
notatior and Navarretia fossalis, which
provided little economic analysis of the
loss of potentially developable acreage
and instead emphasized administrative
costs and impacts to public works
projects. The commenter further states
that the Service should develop
consistent procedures for preparing
economic analyses so that results
between species are comparable,
especially for areas such as the San
Jacinto River, where occupied habitat
for all three of these species overlap.
Our Response: Every economic
analysis of proposed critical habitat
rulemakings is undertaken following the
same framework, described in pages 1–
1 through 1–11 of the DEA. The reports
focus on the economic activities
identified in the proposed rule as likely
to threaten the habitat and resulting in
the greatest impacts. These activities,
and the associated measures required to
minimize impacts, will vary depending
on the attributes of the habitat and the
specific species. Urban development is
identified in the proposed rule as a
threat to Brodiaea filifolia throughout
much of the proposed critical habitat.
As discussed in paragraphs 91 to 95 of
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the DEA, off-setting compensation for
impacts to B. filifolia in essential habitat
areas is based upon mitigation
requirements for the plant contained
within HCPs prepared pursuant to the
NCCP Act of 2001 in California. These
plans primarily require avoidance or
call for conservation of the occurrences
encompassed within the essential
habitat areas identified in the proposed
rule. This is in contrast to potential
mitigation for Atriplex coronata var.
notatior and Navarretia fossalis, for
which developers are able to mitigate
off-site and continue with planned
projects.
(50) Comment: One commenter states
that the DEA fails to address the greatest
capital expenditure in western Riverside
County, because it does not include the
costs required to purchase and maintain
reserves for the species. The comment
further states that costs of restoring
current habitat that could be lost to
land-altering activities on private lands
should also be included.
Our Response: The Western Riverside
County MSHCP is a comprehensive,
multi-jurisdiction HCP for conservation
of species and their habitats in Western
Riverside County. Under the Plan, we
will grant take authorization under
Section 10(a)(1)(B) of the Act for
otherwise lawful activities such as
private development that may
incidentally take or harm listed wildlife
species in exchange for assembly and
management of an MSHCP Conservation
Area. The MSHCP Conservation Area
will be formed through a variety of
methods, including inclusion of existing
conservation banks and/or mitigation
areas, establishment of new
conservation banks and/or mitigation
areas, incentives provided to private
landowners to voluntarily convey their
property for conservation, purchase of
lands through the Local Development
Mitigation Fee paid by project
applicants seeking coverage, or direct
purchase of land by the project
proponent as an in-lieu payment. As
stated in paragraph 94, based in part on
the requirements of the MSHCP, the
analysis assumes that 95 percent of
Brodiaea filifolia habitat in areas
susceptible to development activity are
preserved. The costs of preserving these
areas, along with the costs of relocating
the plant, salvaging bulbs, and
maintaining and monitoring
populations for the remaining five
percent of affected development, is
captured in the analysis.
(51) Comment: One commenter
questions the use of the IMPLAN model,
given the DEA’s caveat that the model
overstates the long-term impacts of
regulatory change.
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Our Response: Input-output models
are discussed as an example of one tool
commonly used by economists to
estimate regional impacts. However, this
particular tool is not used in this
analysis. Instead, the DEA relies on a
partial equilibrium model to estimate
regional effects.
(52) Comment: One commenter states
that Exhibit ES–2 in the DEA should
provide administrative costs as a
separate line item.
Our Response: Exhibit ES–2 provides
information to the reader concerning
key impacts of the designation,
including activities that may be most
impacted by Brodiaea filifolia
conservation efforts. Administrative
costs are included in the cost estimates
for each activity presented, rather than
reported separately, because they
represent only 2 percent of upper-bound
total costs estimated for proposed
critical habitat. In present value terms
assuming a 7-percent discount rate,
these administrative costs are
approximately $272,000; assuming a 3percent discount rate, administrative
costs total $298,000.
(53) Comment: Several commenters
question the DEA’s inclusion of units/
subunits 1b, 2, 4d, 4e, 8b, 8e, 10, EH–
1, EH–2, EH–3, and EH–7 (as listed in
the DEA) in the development analysis.
The comments state that developmentrelated impacts in these units are
unlikely, because either these units have
already been developed or they are
permanently preserved open space.
Our Response: The DEA utilized the
best available information locating
developable land within areas
containing features essential to the
conservation of Brodiaea filifolia. This
information includes a geographic
information systems (GIS) layer from the
San Diego Association of Governments
(SANDAG) locating developable land
within essential habitat units in San
Diego County, and a GIS layer from the
Southern California Association of
Governments (SCAG) locating vacant
land within essential habitat units in
Los Angeles, San Bernardino, Orange,
and Riverside Counties. Because the
SANDAG and SCAG data are updated
only every few years, it is possible that
information for certain parcels is no
longer current. Accordingly, the Service
appreciates the new information
provided during the public comment
period that allows for a refinement of
the DEA. Based on this information, the
calculation of development impacts was
revised to remove all of the units listed
above, with the exception of subunit 1b.
Subsequent research has shown that the
subunit is privately owned, not
developed, and the plants are not
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currently located in a preserve. Note
that all of the above referenced areas,
except subunit 1b, have been removed
or excluded from the final designation.
(54) Comment: One commenter states
that the methodology should be refined
so that the bias of overstatement in the
analysis can be eliminated.
Our Response: The potential impacts
of Brodiaea filifolia conservation
activities on development within
essential habitat are a function of the
distribution of the plant within the unit,
the ability of the developer or
landowner to modify projects to avoid
each locality, and the existence of
alternative uses of the property that do
not threaten the plant, all of which are
unknown. The DEA uses the best
available information to quantify
potential impacts in light of the
uncertainty associated with these
factors.
(55) Comment: Two commenters state
that there should be no additional costs
associated with designating critical
habitat in areas covered by approved
HCPs. In particular, one comment states
that many of the Federal Information
Processing Standard (FIPS) places
discussed in Exhibit 3–11 are included
within approved HCPs and should be
deleted from the analysis.
Our Response: We recognize that
many of the FIPS listed in Exhibit 3–11
are located within approved or pending
HCP jurisdictions and that these plans
may require protection of Brodiaea
filifolia habitat. However, as stated in
the DEA, costs incurred due to
conservation activities and other
protective measures carried out by other
Federal agencies, State and local
governments, and other parties are
considered co-extensive with the
protection offered by critical habitat.
Inclusion of co-extensive impacts in the
economic analysis complies with
direction from the U.S. Tenth Circuit
Court of Appeals.
(56) Comment: One commenter states
that the DEA should estimate costs
associated with the potential loss of
redevelopment increment funds in the
City of San Marcos, because a majority
of land in the proposed critical habitat
within the City occurs in an adopted
Redevelopment Project Area.
Our Response: Based on recent
conversations with the City of San
Marcos, we agree that redevelopment
increment funds may be impacted if
property construction is reduced in
areas where funds would have been
collected by San Diego County and
allocated to the City. However, the city
representatives were not able to provide
information about the potential
magnitude of the impact.
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(57) Comment: One commenter states
that the DEA should factor in costs of
the proposed designation to
infrastructure assessment districts in the
City of San Marcos.
Our Response: We agree that impacts
associated with reduced or delayed
development in infrastructure
assessment districts within the City of
San Marcos are a possibility.
Infrastructure assessment districts
include Community Facilities Districts
or Special Assessment Districts that levy
additional taxes on properties within
the district to finance the construction
of public facilities. The additional tax
for each included property may be
based on a variety of factors such as lot
size and benefit received by the
property. Therefore, Brodiaea filifolia
conservation activities may reduce taxes
received by a particular district where
new property construction that would
occur absent the designation does not
occur. However, an estimate of the
degree of this reduction would require
information on the type and value of
future development at a parcel-specific
level. This information is currently
unknown.
Because the tax is used by the City to
make payments on bonds issued to
finance construction of public facilities,
Brodiaea filifolia conservation activities
may also impact the City, developers,
and bondholders where development
projects associated with special
assessments are halted after bond
issuance, leading to property
indebtedness in which the developer is
unable to finance its portion of the
project and/or the City is unable to
make payments to bondholders. The
potential for B. filifolia conservation
activities to render the developer and/or
the City unable to meet its financial
obligations is a function of currently
unknown variables such as the location
of B. filifolia on the project site, project
specifications, and the financial status
of the developer and/or the City.
(58) Comment: One commenter states
that the development analysis is
inaccurate, because it uses residential
land values even though a number of
the proposed critical habitat units in the
City of San Marcos are zoned for nonresidential uses. Specifically, the
commenter states that the DEA does not
factor in values of parcels that are zoned
for industrial use in subunits 8c, 8d, and
8e. It also questions the appropriateness
of the impact scenarios based on
‘‘supply of housing’’ and ‘‘home prices’’
in these areas. Another comment states
that the per-acre land values estimated
in the DEA and presented in Exhibit 3–
7 appear low.
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Our Response: The first scenario
analyzed in the DEA captures potential
losses to owners of developable parcels
zoned for non-residential uses. This
scenario assumes that in areas that must
be avoided, or set-aside, from future
development, the market value of those
acres is lost. The market value of raw
land implicitly incorporates all
potential future uses of the property, be
it residential, commercial, industrial, or
otherwise. Thus, the loss in land value
captures the lost value of future use of
the property. The sample of property
values used in this analysis includes a
mix of properties zoned for residential
and non-residential uses and therefore
is reasonably representative of losses on
average.
Market values used in the DEA are
drawn from a data set of raw land values
obtained from the San Diego County
assessor for parcels located within areas
containing features essential to the
conservation of Brodiaea filifolia. Based
on conversations with the assessor, to
ensure that assessed values of raw land
were consistent with market values, the
DEA uses a sample from this dataset
including only parcels sold and
assessed in 2004. This sample includes
parcels zoned for industrial use in
subunit 8d. Considering public
comment, an adjustment is made to the
final analysis. In the DEA, the per-acre
land value was calculated as a weighted
average across the sample of parcels.
This approach may understate per-acre
values due to the presence of several
parcels of relatively low value and high
acreage in the sample. The economic
analysis was revised, calculating a peracre value based on the average of the
per-acre values implied by each parcel,
and by eliminating an outlying parcel
from the sample. This revision results in
a per-acre average land value for parcels
in San Diego County of $69,000.
We note that the second scenario
estimated in the DEA (paragraphs 100
through 109), which measures consumer
welfare losses associated with higher
home prices, does not consider the
impact of shifts in prices of commercial
or industrial facilities. Analysis under
the second scenario relies on an existing
economic model estimating the shift in
quantity of housing supplied as a result
of critical habitat. No such model exists
for non-residential development,
therefore we are unable to estimate
welfare losses in markets for
commercial or industrial properties at
this time.
(59) Comment: One commenter states
that the DEA contains a misreading of
the San Diego County MHCP standards
as summarized in Exhibit 3–6.
According to the comment, inclusion in
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a soft-line area by and of itself does not
dictate the high conservation standards
of 95 percent provided in Exhibit 3–6
unless that population is also deemed to
be critical by the MHCP. The comment
notes that Brodiaea filifolia occurrences
in the City of Carlsbad are located in a
Major Amendment Area and not in a
soft- or hard-line area. Another
comment states that the DEA overlooks
the relative importance of each of the B.
filifolia localities and how this could
affect compensation within
conservation plans for the species.
Our Response: Information on
conservation measures for Brodiaea
filifolia contained in the MHCP relies on
personal communication with the
County, as noted in Exhibit 3–6. The
sample of conservation requirements
reviewed in this exhibit represent the
best available information regarding
uncertain future conservation
requirements in areas, both within these
plans and outside the boundaries. As
discussed in paragraph 94, the analysis
assumes that the highest level of
conservation for B. filifolia provided
across the approved plans will apply to
future development projects. Given the
uncertainty regarding the location of
plants, the significance of particular
populations, and the configuration of
specific development projects, this
assumption may overstate impacts for
specific projects.
(60) Comment: One commenter
questions the disparity between costs
for particular units. The commenter
states that subunit 8d is in the center of
the City of San Marcos while the Miller
Mountain unit (subunit 5a) is on private
and Forest Service land within the San
Mateo Wilderness. For this reason, the
commenter questions why the estimated
costs for subunit 8d are low, relative to
the estimated costs for the Miller
Mountain property.
Our Response: The relative costs to
development activities assigned to each
unit are a function of the land value
losses calculated in the first scenario
and the impacts to the housing market
calculated in the second scenario. In the
first scenario, costs are driven by the
quantity of private, developable land
within the unit that is projected to be
developed in the next 20 years. As
shown in Exhibit 3–8, proposed subunit
8d contains 18.64 acres of projected
development on private, developable
acres while subunit 5a contains 21.36
acres; therefore, impacts under this
scenario are greater for subunit 5a.
In the second scenario, impact
estimates are driven by the overall
amount of new housing anticipated in
the FIPS place closest to the unit and
median home values in that FIPS place
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(FIPS places generally follow the legal
boundaries of incorporated cities). The
DEA assigned subunit 5a to the closest
FIPS place, San Clemente and subunit
8d to San Marcos. The disparity in
impacts estimated in this scenario
results from difference in the median
home price and projected number of
future houses in the two cities.
However, based on public comment and
further reflection, a new assumption is
applied to this scenario.
Some areas of essential habitat, such
as subunit 5a, fall outside the
boundaries of the 10 FIPS places
included in the DEA. Several of these
units fall within 3 miles of the nearest
FIPS place and thus are assigned to that
place. Five remaining units, including
subunit 5a, are 10 or more miles from
the nearest FIPS place. Zabel and
Paterson’s model, described in
paragraph 101 and used to estimate
market impacts, represents the best
available tool for estimating impacts to
the housing market resulting from
critical habitat designation. However,
this tool is not capable of assigning costs
to these five units. Considering their
more remote nature, as demonstrated by
their distance from densely populated
areas, designation is less likely to result
in substantial impacts relevant to the
housing market. Because the potential
magnitude of market effects is unknown
for these five areas, no consumer
welfare losses are reported for these
areas in the final economic analysis.
(61) Comment: One commenter states
that the development analysis should
evaluate a scenario of higher density
development along with the benefits of
adjacent open space conservation.
Our Response: The DEA analyzes two
scenarios, as described in paragraphs 80
through 109. The first scenario assumes
that no future housing stock is lost due
to Brodiaea filifolia conservation
activities, because substitute sites are
available. The second scenario assumes
that some future housing stock is lost
(e.g., not constructed at other sites).
Adding a third scenario of higher
density development, as suggested by
the comment, would result in an impact
estimate similar to the estimate in the
first scenario, and no larger than
estimated in the second. Higher density
development represents a substitution
option similar to the availability of noncritical habitat developable land. It
assumes that the same number of homes
are built, but simply on a smaller
footprint. In addition, such a scenario
might require the assumption that
existing zoning-related restrictions will
be lifted to accommodate the higher
density development. We have no
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information to suggest such a change in
existing regulation will occur.
If higher density development results
from Brodiaea filifolia conservation
activities, additional open space may be
preserved. Various studies document
the positive effect of environmental
amenities, including open space, on the
value of nearby residential and
commercial properties (e.g., Thibodeau
and Ostro (1981), Nelson (1985), Lacy
(1990), Garrod and Willis (1992),
Bockstael (1996), Geoghegan (1998),
Acharya and Bennet (2001)). The
enhancement of real estate values
depends on, among other things, the
proximity of homes to open space and
the spatial extent of the effect (only the
homes immediately adjacent to the
space are affected, the entire
neighborhood is affected, or the entire
town or region is affected), whether the
effect decreases with distance from the
open space and at what rate, whether
the community already contains a
significant supply of conserved land,
and the relationship between local
development pressure and values for
conserved open space (e.g., if open
space is scarce, and development
pressure high, the combination could
affect the magnitude of the benefit).
To make a defensible transfer of
‘‘open space value’’ as identified in the
literature to a community or
neighborhood impacted by Brodiaea
filifolia conservation activities,
additional data are required. For
example, information on the extent of
existing open space in the affected
communities and the additional amount
likely to be conserved as a result of B.
filifolia conservation activities must be
compared to similar statistics for the
communities assessed in the economics
literature. In addition, the transfer
requires an assessment of the
similarities in the quality and attributes
of the land to be conserved with the
qualities and attributes of the land
studied in the literature. The models
and data required to complete this
transfer are not readily available for B.
filifolia habitat. As a result, the DEA is
unable to estimate the potential benefits
of open space conservation.
(62) Comment: One commenter
questions the cost allocation across
units in Exhibit 3–3. The comment
states that, given that the preceding
exhibit (Exhibit 3–2) contains only four
subunits that have had a formal or
informal consultation, it is questionable
as to why the rest of the subunits are
included if they have never been
consulted on.
Our Response: Exhibit 3–3 does not
include units where no consultation has
taken place. Exhibit 3–2 presents a
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summary of consultations for
development projects that occurred in
areas containing features essential to the
conservation of the species in the
proposed rule, but it does not reflect
consultations or project modifications
that have occurred for HCPs. Exhibit 3–
3, on the other hand, presents the past
costs of these development
consultations (administrative and
project modification costs) in addition
to administrative costs of the
development of HCPs that have
jurisdiction over essential habitat areas.
Footnote 45 notes that these HCPs are
the County of San Diego Subarea Plan
under the Multiple Species
Conservation Program (MSCP) in March
1998, the Western Riverside County
MSHCP in June 2004, and the City of
Carlsbad’s Habitat Management Plan
(HMP) under the MHCP in November
2004. As stated in the note (a) to Exhibit
3.3, the analysis distributes the HCP
costs evenly across the units covered by
the plans.
(63) Comment: One commenter asks
whether costs in Exhibit 3–2 are
attributed solely to Brodiaea filifolia or
whether other listed species benefited
from the consultations and mitigation
activities.
Our Response: Exhibit 3–2
summarizes four consultations for
development projects that have
occurred in areas containing features
essential to the conservation of Brodiaea
filifolia in the proposed rule. These
consultations covered other species in
addition to B. filifolia. The consultations
covering subunits 6c and 8b also
considered the coastal California
gnatcatcher, as noted in Exhibit 3–2.
The consultations covering subunit 7a
note that other federally threatened and
State species of special concern occur
onsite, such as the coastal California
gnatcatcher, northern harrier, Cooper’s
hawk, white-tailed kite, and California
adolphia; however, the consultations
were primarily focused on impacts to B.
filifolia. For all of the consultations,
project modification costs described in
the table were driven by efforts to
protect B. filifolia and, therefore, are
attributed to this species.
(64) Comment: One commenter states
that, typically, the developer will pass
any increase in project cost to the
ultimate consumer of the development
(homeowner, business owner, building
owner), not to the raw landowner. It is
the experience of the commenter that
developers simply recognize the cost of
building constraints, work with them
and build them into the ultimate cost of
the product.
Our Response: The assumption
referred to in this comment is derived
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from the first development scenario
analyzed in paragraphs 84 and 87
through 99 of the DEA. This scenario
assumes that within regional housing
markets, substitute land exists for
development that would otherwise
occur within essential habitat. Projected
development shifts to less preferred
sites (e.g., areas that were previously
farther out in time on the development
horizon or that were not anticipated to
be developed within the next 20 years).
This assumption may be reasonable for
the proposed designation, because the
potentially affected acres represent a
small percentage of the total
developable land in the municipalities
where they are located. Accordingly,
existing landowners whose land would
otherwise be higher in the hierarchy of
potentially developable sites must
accept lower prices associated with
Brodiaea filifolia conservation activities
if development is to occur. This
assumption is consistent with peer
review by three economists of previous
economic analyses of proposed critical
habitat in California. Note that the
second development scenario (described
in paragraphs 100 through 109) makes
the alternative assumption that land is
scarce. Under this scenario, homebuyers
experience costs associated with B.
filifolia conservation activities.
(65) Comment: One commenter states
that Exhibit 5–3 is flawed because not
every unit contains a transportation
issue. The commenter requests that a
more realistic transportation scenario be
evaluated based on specific subunits.
Another commenter states that the
transportation impacts analysis is
incomplete, because the Service did not
contact the Riverside County
Transportation Commission or the local
cities to identify transportation projects
in areas containing features essential to
the conservation of Brodiaea filifolia.
Our Response: We acknowledge that
simplifying assumptions were made in
the DEA to bound the potential
magnitude of transportation-related
impacts. During development of the
DEA, the relevant district offices of
California Department of Transportation
(CALTRANS), which has responsibility
for transportation-related projects in
California, were contacted (see
paragraphs 126 through 130).
CALTRANS represents the best publicly
available source of State transportation
projects. The offices were unable to
provide site-specific information about
the potential location of future Brodiaea
filifolia conservation activities.
Therefore, the DEA used a historical rate
of consultation, plus information about
the project modifications associated
with those consultations, to predict
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future transportation costs. These
impacts were assumed to be equally
likely to occur in any unit (excluding
lands on Camp Pendleton), resulting in
an even distribution of costs shown in
Exhibit 5–3. Note that, based on new
information received during the public
comment period, transportation-related
impacts are removed from units where
B. filifolia is not present, the land is
already preserved, the land is already
developed, or a plan is already in place
to move the plants to another location.
These units include units/subunits
described in the DEA as 2, 4a, 4d, 4e,
8b, 8e, 10, EH–1, EH–2, EH–3, and EH–
7.
Based on this comment, the Riverside
County Transportation Commission was
contacted, and information about
potential impacts associated with the
Highway 79 re-alignment project and
the Mid-County Parkway was requested.
At this time, due to the sensitive nature
of the projects and their early stages, a
representative of the commission was
unable to provide specific information
about whether habitat for Brodiaea
filifolia would be impacted. However,
he noted that if B. filifolia habitat is
identified, project modifications would
likely be similar to conservation
requirements found in the Western
Riverside County MSHCP. In areas
containing features essential to the
conservation of the plant, information
from cities about potential
transportation-related impacts is not
readily available at this time.
(66) Comment: One commenter states
that the DEA ignores the costs
associated with designing, refining, and
negotiating a preferred alternative to
avoid Brodiaea filifolia in the FoothillSouth Corridor. The commenter also
states that the DEA ignores mitigation
measures specially designed to address
potential B. filifolia impacts, such as
focused plant surveys, seed collection
and salvage measures, soils collection
and translocation, and translocation
monitoring. Finally the commenter
states that the DEA also ignores delay
costs.
Our Response: As discussed in
paragraphs 123 through 125, the DEA
considered impacts to the FoothillSouth project. At that time, the best
information available suggested that the
preferred alternative would completely
avoid Brodiaea filifolia habitat.
However, new information has since
been provided by the Transportation
Corridor Agencies (TCA), the
organization responsible for this project.
Specifically, TCA stated that three
populations will be affected by the
project and provided information about
past costs, future mitigation costs, and
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potential delay costs. These costs were
incorporated in the final economic
analysis. The three units where B.
filifolia populations are anticipated to
be affected by the Foothills-South
project are subunits 4c, 4f, and 4h. All
three of these units are excluded from
the final designation.
(67) Comment: One commenter states
that Exhibit 5–4 of the DEA may be
flawed, because not every unit contains
a utility corridor. The commenter
requests that a more comprehensive
subunit evaluation of potential impacts
to utility projects be conducted.
Our Response: We acknowledge that
simplifying assumptions are made in
Section 5.2 in order to bound the
analysis of impacts to utility activities.
A rapid assessment of transmission
lines and distribution systems operated
by San Diego Gas and Electric was
conducted in order to extrapolate
potential impacts across San Diego and
Orange counties. Therefore, actual
future costs to utility activities may be
higher or lower in certain units
presented in Exhibit 5–4. However, the
costs presented in the final economic
analysis represent the best available
information at this time. Also note that,
based on new information received
during the public comment period,
utility-related impacts are removed from
units where Brodiaea filifolia is not
present, the land is already preserved,
the land is already developed, or a plan
is already in place to move the plants to
another location. These units include 2,
4a, 4d, 4e, 8b, 8e, 10, EH–1, EH–2, EH–
3, and EH–7.
(68) Comment: One commenter states
that the DEA should consider the
proposed Special Area Management
Plan (SAMP) for the San Jacinto
watershed and potential economic
impacts of the critical habitat
designation within the watershed.
Our Response: The ACOE is currently
conducting a comprehensive aquatic
resource plan, called a SAMP, for the
San Jacinto watershed. The purpose of
the SAMP is to establish a watershedwide aquatic resource reserve program,
and to minimize individual and
cumulative impacts of future projects in
this watershed. The SAMP will result in
the issuance of programmatic and
individual permits issued under section
404 of the Clean Water Act. Because the
sensitive areas identified by the SAMP
are likely to overlap critical habitat, the
SAMP will not provide significant new
information about the sensitivity of
these acres. In addition, because the
DEA assumes that 95 percent of habitat
for Brodiaea filifolia that is likely to be
developed in the next 20 years will be
avoided (see paragraph 94), it is
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73833
unlikely that more burdensome actions
will be required by the ACOE as a result
of the SAMP. Therefore, the cost
estimates calculated in the DEA are
unlikely to be affected by the SAMP.
(69) Comment: One commenter states
that the DEA should offer some cost
estimates of the proposed flood control
project discussed at paragraph 139.
Our Response: Section 5.3 of the DEA
considers impacts to flood control
activities in areas containing habitat for
Brodiaea filifolia proposed for critical
habitat designation. The best available
data were utilized at the time to
estimate these potential impacts. While
we agree that B. filifolia-related
conservation costs are likely, no
additional information has become
available since the drafting of the DEA
that would allow us to quantify or
monetize these impacts. The units
potentially affected, EH5, EH6, and EH7,
are excluded from the final designation.
(70) Comment: One commenter
offered the following clarification to
page 2–17, section 2.5, paragraph 71: ‘‘It
is incorrect to assume that CEQA
requires a lead agency to ‘presume that
a project will result in a potentially
adverse environmental impact and to
prepare an EIR* * *.’ Rather, CEQA
requires that a project’s impacts be
disclosed, and those disclosed impacts
mitigated to a point beneath a level of
significance. If the project is unable to
do so, then an EIR is required when
determined by the lead agency. A
predisposition towards EIR preparation
regardless of threshold determination is
counter to CEQA precedence.’’
Our Response: We have incorporated
this clarification into the final economic
analysis.
(71) Comment: One commenter
offered the following clarification to
page 2–17, section 2.5, paragraph 73:
‘‘Please note that the Service is an
integral participant in the NCCP
process. Witness that all letters to
participating municipalities are signed
by both the CDFG and the Service.’’
Our Response: We appreciate the
clarification and have incorporated it
into the final economic analysis.
(72) Comment: One commenter noted
that Exhibit 6–2 appears to project costs
to conservancies from 2006–2024, but it
is not clearly stated in the table or text.
Our Response: We have clarified this
in the final economic analysis.
Summary of Changes From Proposed
Rule
In developing the final critical habitat
designation for Brodiaea filifolia, we
reviewed peer and public comments
received on our proposed rule and draft
economic analysis; conducted further
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evaluation of lands included in our
proposal; and refined our mapping
boundaries. This final rule reflects
refinements of our mapping process,
and removal of areas from critical
habitat designation under section
3(5)(A), exemption under section
4(a)(3), and exclusions under section
4(b)(2) of the Act.
We refined our mapping to better
delineate habitat containing features
essential to the conservation of the
species. For example, we found that
there were areas within the boundaries
of proposed critical habitat that did not
contain the physical or biological
features essential to the conservation of
Brodiaea filifolia such as roads and
buildings. In most cases developed areas
were captured in the proposed critical
habitat boundaries because we used a
328 ft (110 m) minimum grid cell size.
When preparing this final designation,
we identified areas where the majority
of a grid cell included developed areas,
then removed these particular cells from
the boundaries of critical habitat. These
refinements reduced the amount of land
in subunit 6d (Taylor/Darwin) and
subunit 8d (Upham) (Table 1) that
contain features essential to the
conservation of the species.
Along with refining our mapping, we
re-evaluated the occurrences of
Brodiaea filifolia included in proposed
critical habitat. Criteria used to
determine if an occurrence is significant
included: occupied habitat supporting a
minimum of 850 naturally occurring
individuals of B. filifolia and/or
populations associated with unique
habitats (e.g. soils, vegetation, or
elevation) or peripheral populations
important for protecting genetic
variability across the species’ range.
Based on our review and reevaluation, a total of 12 units/subunits
were removed from consideration
because we determined they were not
significant occurrences (see ‘‘Criteria
Used to Identify Critical Habitat’’).
Units/subunits removed from
consideration because we determined
they did not support significant
occurrences of Brodiaea filifolia
include: Unit 3 (Aliso Canyon), 4a
(Arroyo Trabuco), 4d (Prima
Deschecha), 4e (Forster Ranch), 4f
(Talega/Segunda Deschecha), 4h
(Christianitos Canyon South), 4i (Blind
Canyon), 6a (Alta Creek), 6c (Oceanside/
Mission Avenue), 7b (Rancho Carrillo),
8a (Rancho Santa Fe Road North), and
8c (Grand Avenue).
Unit 2 (Arrowhead Hot Springs Unit)
was removed from the final designation
because it was incorrectly mapped.
Although the proposed rule correctly
describes the Arrowhead Hot Springs
unit in the text, the map provided in the
proposed rule depicted an area known
as Waterman Canyon.
Subunits 8e (Linda Vista), 9 (Double
LL Ranch), and 10 (Highland Valley)
were removed from consideration
because we could not verify reported
occurrences of Brodiaea filifolia.
We removed subunit 5a (Miller
Mountain) from consideration because
the plants in this area are mostly
hybrids between Brodiaea filifolia and
Brodiaea orcuttii (Boyd et al. 1992). No
information is available regarding the
number of pure B. filifolia within this
occurrence and whether they can be
considered as contributors to the longterm conservation of the species.
We removed a portion of lands in
subunit 5b (Devil Canyon) from
consideration because the area is not
known to be occupied by Brodiaea
filifolia.
We removed subunit 8b (Rancho
Santalina/Loma Alta) from
consideration under section 3(5)(A) of
the Act because it is already receiving
special management considerations (see
the ‘‘Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the
Act’’).
We removed 205 ac (83 ha) of land in
Riverside County identified in the
proposed rule as containing features
essential to the conservation of the
species, but which were excluded under
section 4(b)(2) of the Act. The lands
removed were near Corona and in
Moreno Valley. We removed these areas
because they are not known to be
occupied by Brodiaea filifolia.
Approximately 3,062 ac (1,234 ha) of
land in Riverside County containing
features essential to the conservation of
B. filifolia are excluded under section
4(b)(2) of the Act.
Six units/subunits are being excluded
under section 4(b)(2) of the Act. Three
subunits, including 4b (Casper’s Park),
4c (Canada/Gobernadora), and 4g
(Christianitos Canyon) are within the
boundaries of the pending Orange
County Southern Subregion NCCP/HCP,
which includes the participation of the
County of Orange and Rancho Mission
Viejo, both of which are parties to a
Settlement Agreement for the Ranch
Plan. Subunits 6b (Mesa Drive) and 6d
(Taylor/Darwin) are within the
boundaries of the pending City of
Oceanside Subarea Plan of the
Northwestern San Diego County MHCP.
Subunit 7a (Fox-Miller) is covered
under the City of Carlsbad’s approved
HMP.
In this final rule, lands on Camp
Pendleton that were excluded from
proposed critical habitat under section
4(b)(2) of the Act are now exempt
pursuant to section 4(a)(3) of the Act.
For more discussion about the areas
exempted or excluded from this final
designation, please refer to the section
‘‘Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the
Act.’’
Overall, these refinements, removals,
exemptions and exclusions resulted in a
reduction from 4,690 ac (1,898 ha)
included in the proposed designation to
597 ac (242 ha) included in the final
designation (see Table 1 below).
Critical habitat unit/subunit
County
Proposed critical habitat
(ac; ha)
Unit 1: Los Angeles County .....................................................................
1a: Glendora .....................................................................................
1b: San Dimas ..................................................................................
Unit 2: Arrowhead Hot Springs ................................................................
Unit 3: Aliso Canyon ................................................................................
Unit 4: Orange County .............................................................................
4a: Arroyo Trabuco ...........................................................................
4b: Casper’s Wilderness Park ..........................................................
˜
4c: Canada Gobernadora/Chiquita Ridgeline ...................................
4d: Prima Deschecha .......................................................................
4e: Forster Ranch .............................................................................
4f: Talega/Segunda Deshecha .........................................................
4g: Cristianitos Canyon ....................................................................
4h: Cristianitos Canyon South ..........................................................
4i: Blind Canyon ...............................................................................
Los Angeles ............
.................................
.................................
San Bernardino .......
.................................
Orange ....................
.................................
.................................
.................................
.................................
.................................
.................................
.................................
.................................
.................................
Total 294; 119 ................
96; 39 .............................
198; 80 ...........................
89; 36 .............................
151; 61 ...........................
Total 1,860; 753 .............
74; 30 .............................
259; 105 .........................
311; 126 .........................
119; 48 ...........................
96; 39 .............................
190; 77 ...........................
588; 238 .........................
72; 29 .............................
151; 61 ...........................
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E:\FR\FM\13DER2.SGM
13DER2
Final critical habitat
(ac; ha)
Total 294; 119
96; 39
198; 80
0
0
Total 0
0
0
0
0
0
0
0
0
0
Federal Register / Vol. 70, No. 238 / Tuesday, December 13, 2005 / Rules and Regulations
73835
Critical habitat unit/subunit
County
Proposed critical habitat
(ac; ha)
Unit 5: Northern San Diego County .........................................................
5a: Miller Mountain ...........................................................................
5b: Devil Canyon ..............................................................................
Unit 6: Oceanside ....................................................................................
6a: Alta Creek ...................................................................................
6b: Mesa Drive .................................................................................
6c: Oceanside East/Mission Avenue ................................................
6d: Taylor/Darwin ..............................................................................
Unit 7 .......................................................................................................
7a: Fox-Miller ....................................................................................
7b: Rancho Carrillo ...........................................................................
Unit 8: San Marcos ..................................................................................
8a: Rancho Santa Fe Road North ....................................................
8b: Rancho Santalina/Loma Alta ......................................................
8c: Grand Avenue ............................................................................
8d: Upham ........................................................................................
8e: Linda Vista ..................................................................................
Unit 9: Double LL Ranch .........................................................................
Unit 10: Highland Valley ..........................................................................
San Diego ...............
.................................
.................................
.................................
.................................
.................................
.................................
.................................
.................................
.................................
.................................
.................................
.................................
.................................
.................................
.................................
.................................
.................................
.................................
Total 1,527; 618 .............
1,263; 511 ......................
264; 107 .........................
Total 198; 81 ..................
49; 20 .............................
5; 2 .................................
64; 26 .............................
80; 32 .............................
Total 125; 50 ..................
93; 38 .............................
32; 13 .............................
Total 315; 127 ................
86; 35 .............................
82; 33 .............................
10; 4 ...............................
117; 47 ...........................
20; 8 ...............................
57; 23 .............................
74; 30 .............................
Total 249; 101
0
249; 101
Total 0
0
0
0
0
Total 0
0
0
Total 54; 22
0
0
0
54; 22
0
0
0
Total ...........................................................................................
.................................
4,690; 1,898 ...................
597; 242
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’’ means the use
of all methods and procedures that are
necessary to bring an endangered or a
threatened species to the point at which
listing under the Act is no longer
necessary.
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 requires consultation
on Federal actions that may 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.
To be included in a critical habitat
designation, the habitat must contain
the physical and biological features
essential to the conservation of the
species. Critical habitat designations
identify, to the extent known using the
best scientific data available, areas that
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provide for the essential life cycle needs
of a species (i.e., areas on which are
found the primary constituent elements,
as defined at 50 CFR 424.12(b)).
Habitat occupied at the time of listing
may be included in critical habitat only
if the essential features thereon may
require special management or
protection. Thus, we do not include
areas where existing management is
sufficient to conserve the species. (As
discussed below, such areas may also be
excluded from critical habitat pursuant
to section 4(b)(2).) 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 was 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 and commercial data
available. They require Service
biologists to the extent consistent with
the Act and with the use of the best
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Final critical habitat
(ac; ha)
scientific and commercial 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.
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
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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)(1)(A) of
the Act, we used the best scientific data
available in determining areas that are
essential to the conservation of Brodiaea
filifolia. We used data and information
contained in, but not limited to, the
proposed listing rule (59 FR 64812,
December 15, 1994); the final listing
rule (63 FR 54975, October 13, 1998);
data and information from research and
survey observations in published, peerreviewed articles; data provided by the
California Department of Fish and Game
(CDFG); and data provided by the
California Natural Diversity Database
(CNDDB); data and information
included in reports submitted during
section 7 consultations; information
contained in species analyses for
individual and regional HCPs where B.
filifolia is a covered species or is being
proposed for coverage; data collected on
Camp Pendleton; data collected from
reports submitted by researchers
holding section 10(a)(1)(A) recovery
permits; and information received from
local species experts. We also used
information contained in comments
received during the comment periods
for the proposed rule and the draft
economic analysis.
We are not designating areas outside
the geographical areas known to be
occupied by the species and identified
in the final listing rule (63 FR 54975).
The listing rule noted that populations
were centered in the cities of Vista, San
Marcos, and Carlsbad in San Diego
County, in the vicinity of the Santa Rosa
Plateau in Riverside County, with
additional ‘‘scattered’’ populations in
Orange, Los Angeles, Riverside, San
Bernardino, and San Diego counties.
Critical habitat is not being designated
in San Bernardino, Orange and
Riverside counties. Areas in Los
Angeles and San Diego counties
designated as critical habitat and listed
in Table 1 are within the geographical
areas known to be occupied by the
species.
Habitat that contains the features
essential to the conservation of the
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species was delineated by examining (1)
species occurrence information in Los
Angeles, San Bernardino, Orange,
Riverside, and San Diego counties from
the CNDDB and from survey reports; (2)
vegetation data layers from Orange,
Riverside, and San Diego counties and
vegetation data layers from the U.S.
Forest Service’s Cleveland National
Forest for Los Angeles and San
Bernardino counties; (3) Natural
Resources Conservation Service’s Soil
Survey Geographic Database (SSURGO)
soil data layers for Orange, Riverside,
and San Diego counties, and State Soil
Geographic Database (STATSGO) soil
data layers for Los Angeles and San
Bernardino counties; and (4) slope data
derived from a 30-meter digital
elevation model (DEM). These layers
were overlaid on digital ortho quarter
quadrangle (DOQQ) satellite imagery
layers, and habitat was delineated in
areas that had an extant species
occurrence within them, had not
undergone development, had the PCEs,
including suitable soil and vegetation
types, and had a slope of less than 20
degrees. After creating a GIS coverage of
the essential areas, we created legal
descriptions of these areas. We used a
100-meter grid to establish Universal
Transverse Mercator (UTM), North
American Datum (NAD) 27 coordinates
which, when connected, provided the
boundaries of the areas containing
features essential to the conservation of
the species.
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 are
required to base critical habitat
determinations on the best scientific
and commercial data available and to
consider those physical and biological
features, otherwise referred to as
primary constituent elements (PCEs),
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,
rearing of offspring, germination, seed
dispersal; and generally habitats that are
protected from disturbance or are
representative of the historic
geographical and ecological
distributions of a species. The specific
PCEs required for Brodiaea filifolia 1⁄2
are derived from the physical and
biological needs of the species as
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described below and in the final listing
rule (63 FR 54975, October 13, 1998).
Brodiaea filifolia is a perennial herb
in the Liliaceae (lily family) that
annually produces leaves and flower
stalks from underground corms
(underground bulb-like storage stem).
Corms are dormant in the summer, but
leaves begin growing after the first
significant rains in the fall saturate the
soil. At the time of flowering, the leaves
of B. filifolia are dead or nearly so. The
flowering period lasts for two to three
weeks in late spring to early summer.
Young plants produce only leaves for a
few seasons before being capable of
producing flower stalks. Even mature
specimens may not flower every year,
depending upon environmental
conditions. It is estimated that about 10
percent of all specimens flower in an
average rainfall year (Vince Scheidt in
litt. 2005). The six perianth segments are
violet, with their tips spreading. The
staminodia (characteristic sterile
stamens) are narrow and pointed.
All species of Brodiaea are selfincompatible (incapable of producing
seeds with pollen from flowers on the
same plant or from flowers on plants
with the same allele at the selfincompatibility locus), requiring crosspollination from plants of the same
species but with different alleles at this
locus. Dispersal of seeds from an
individual is likely localized, leading to
patches of plants with the same selfincompatible alleles. This means that
effective pollination for seed set
requires pollen dispersal over a distance
between plants with different selfincompatible alleles. Likewise, this
necessitates maintenance of pollinator
habitat and dispersal corridors. The
vegetative production of small cormlets
by the corm is the principal means by
which plants of the genus Brodiaea
perpetuate themselves (Niehaus 1971).
Members of the genus Brodiaea likely
rely on Tumbling Flower Beetles
(Mordellidae, Coleoptera) and Sweat
Bees (Halictidae, Hymenoptera) for
cross-pollination (Niehaus 1971). The
home ranges and species fidelity of
these pollinators is not known. Bell and
Rey (1991) report that native bees
observed pollinating Brodiaea filifolia
on the Santa Rosa Plateau in Riverside
County included Bombus californicus
(Apidae, Hymenoptera), Hoplitus sp.
(Megachilidae, Hymenoptera), Osmia
sp. (Megachilidae, Hymenoptera), and
an unidentified Anthophorid (diggerbee). Anthophoridae and Halictidae are
reported to be important pollinators of
B. filifolia at a study site in Orange
County (Glen Lukos Assoc. 2004).
Alternative pollen source plants may be
necessary for the persistence of these
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insects when B. filifolia is not in flower
seasonally or annually because of poor
environmental conditions.
Studies to quantify the distance that
bees will fly to pollinate their host
plants are limited in number, but the
few that exist show that some bees will
routinely fly from 328 to 984 feet (ft)
(100 to 500 meters (m)) to pollinate
plants (Thorp and Leong 1995; Schulke
and Waser 2001). In a study of
experimental isolation and pollen
dispersal of Delphinium nuttallianum
(Nuttall’s larkspur), Schulke and Waser
(2001) report that adequate pollen loads
were dispersed by bumblebees within
control populations and in isolated
experimental ‘‘populations’’ from 328 to
1,312 ft (100 m to 400 m) distant from
the control populations. One of the
several pollinator taxa effective at 1,312
ft (400 m) was Bombus californicus, one
of four bee species observed pollinating
Brodiaea filifolia by Bell and Rey
(1991). Studies by Steffan-Dewenter and
Tscharntke (2000) have demonstrated
that it is possible for bees to fly as far
as 3,280 ft (1,000 m) to pollinate
flowers, and at least one study suggests
that bumblebees may forage many
kilometers from a colony (Sudgen 1985).
The historical range of Brodiaea
filifolia extends from the foothills of the
San Gabriel Mountains in Los Angeles
County, east to the western foothills of
the San Bernardino Mountains in San
Bernardino County, south through
eastern Orange and western Riverside
counties to central (Vince Scheidt in litt.
2005) San Diego County. This species is
usually found in herbaceous plant
communities that occur in open areas
on clay soils, soils with a clay
subsurface, or clay lenses within loamy,
silty loam, loamy sand, silty deposits
with cobbles or alkaline soils, ranging in
elevation from 100 ft (30 m) to 2,500 ft
(765 m), depending on soil series. These
herbaceous communities are generally
classified as annual grassland, valley
needlegrass grassland, valley sacaton
grassland, alkali playa, southern interior
basalt vernal pools, San Diego mesa
hardpan vernal pools, and San Diego
mesa claypan vernal pools (Holland
1986). Based upon dominant species,
these communities have been further
divided into series which include, but
are not limited to, California annual
grassland, nodding needlegrass, purple
needlegrass, foothill needlegrass,
saltgrass, alkali grassland, alkali playa,
and bush seepweed and habitats such as
San Diego mesa vernal pools, San
Jacinto Valley vernal pools, and Santa
Rosa Plateau vernal pools (Sawyer and
Keeler-Wolf 1994). B. filifolia grows in
interstitial areas (often narrow bands of
habitat surrounded by other vegetation)
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in association with coastal sage scrub in
some locations, including portions of
Los Angeles and San Bernardino
counties.
Brodiaea filifolia has also been found
in the San Mateo Wilderness near the
northern border of San Diego and
Riverside counties and in the Miller
Mountain area in the Santa Ana
Mountains of western Riverside County.
These occurrences appear to be mostly
hybrids between B. filifolia and B.
orcuttii, although plants of both species
can also be found. Plants in the San
Mateo Wilderness, mostly hybrid types,
have been observed along the banks of,
and within, intermittent stream
channels. Plants in the Miller Mountain
area have been observed on clay soils in
southern needlegrass grassland (Boyd et
al. 1992). In Miller Canyon, a tributary
that drains the southern flank of Miller
Mountain, B. filifolia and some hybrids
are found on deposits of gravel, cobble,
and small boulders along the stream
channel in association with tussocks of
Juncus macrophyllus (long-leaved rush)
and Muhlenbergia rigens (deer grass)
and in vernal seeps and on open, clay
benches (Boyd et al. 1992).
All members of the genus Brodiaea
appear to require full sun, and many
tend to occur on only one or a few soil
series (Niehaus 1971). In San Diego,
Orange, and Los Angeles counties,
occurrences of Brodiaea filifolia are
highly correlated with specific clay soil
series such as, but not limited to, Alo,
Altamont, Auld, and Diablo or clay lens
inclusions in a matrix of loamy soils
such as Fallbrook, Huerhuero, and Las
Flores series (63 FR 54975, CNDDB
2003, Service GIS data 2004). In San
Bernardino County, the species is
associated with Etsel family-Rock
outcrop-Springdale and Tujunga-Urban
land-Hanford soils (Service GIS data
2004). In western Riverside County, the
species is often found on alkaline siltyclay soil series such as, but not limited
to, Domino, Grangeville, Waukena, and
Willows or on clay loam soils underlain
by heavy clays derived from basalt lava
flows (i.e., Murrieta series on the Santa
Rosa Plateau) (U.S. Department of
Agriculture 1971, Bramlet 1993, CNDDB
2003). On these soils, B. filifolia is
typically found as a component of
native perennial and annual grasslands.
In the City of San Marcos in San Diego
County, and near Hemet and on the
Santa Rosa Plateau in Riverside County,
these grasslands are often part of the
watersheds for vernal pool and playa
complexes (Bramlet 1993; Service 1998;
CNDDB 2005). These soils facilitate the
natural process of seed dispersal and
germination, cormlet disposition to an
appropriate soil depth, and corm
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73837
persistence through seedling and adult
phases of flowering and fruit set
described earlier.
Clay soils dry out and exhibit surface
cracks as surface moisture is depleted
prior to the next rainy season. During
this period the capsules of many bulb
and corm-forming species mature. The
seeds are released to fall to the ground,
either on the surfaces or into the cracks
in the soil. In this manner some seeds
are dispersed into several horizons in
the soil. With the fall and winter rains,
the clay matrix hydrates, softens,
expands and the cracks close up.
Seedlings at first only produce leaves
and a specialized root. Seedlings of
Brodiaea filifolia are equipped with a
specialized succulent contractile root.
This organ, lost by mature corms,
facilitates the seasonal downward
movement of the young plant (Niehaus
1971). The contractile root swells with
moisture in the wet season, creating
space below the developing cormlet. As
the soil dries the contractile root dries
and shrinks longitudinally, drawing the
young cormlet downward in the soil.
This process continues to a point at
which the soil moisture is adequate to
keep the contractile root from shrinking,
resulting in the location of the corm in
the appropriate soil horizon for survival.
Cormlets produced annually from
existing older corms, also produce
contractile roots which draw them
laterally away from the parent corm
(Niehaus 1971).
The size of a particular population of
Brodiaea filifolia and other members of
the species, as well as other corm and
bulb forming species, is often measured
by counting numbers of standing flower
stalks. However, because more plants
flower in wet years than dry years,
flowering plants likely represent only a
portion of the total population of plants
present at any given site. In addition to
the annual fluctuation in numbers of
flowering plants, seedlings and young
plants likely only produce leaves for a
few years before they are able to
produce flower stalks. These vegetative
plants may go undetected in surveys.
Space for Growth of Individuals and
Populations and for Normal Behavior
Habitats with combinations of
appropriate elevation and clay or clay
associated soils, on mesas or low to
moderate slopes that support open
native or annual grasslands within open
coastal sage scrub or coastal sage scrubchaparral communities (PCE 1A), or in
floodplains or in association with vernal
pool or playa complexes that support
various grassland or scrub communities
(PCE 1B), or soils derived from olivine
basalt lava flows on mesas and slopes
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that supports vernal pools with
grassland, oak woodland, or savannah
communities (PCE 1C), or sandy loam
soils derived from basalt and
granodiorite parent material with
deposits of cobbles and boulders
supporting intermittent seeps, and open
marsh communities (PCE 1D), provide
space for the growth and persistence of
Brodiaea filifolia. These habitats also
sustain the pollinators needed for crosspollination.
Food, Water, Air, Light, Minerals, or
Other Nutritional or Physiological
Requirements
A natural generally intact surface and
subsurface structure, not permanently
altered by anthropogenic land use
activities, and associated physical
processes such as a hydrological regime
(PCE 2) is necessary to provide water,
minerals, and other physiological needs
for Brodiaea filifolia. A natural
hydrological regime includes seasonal
hydration followed by drying out of the
substrate to promote growth of active
plants and new corms for the following
season. These conditions are also
necessary for the normal development
of seedlings and young vegetative
cormlets.
The conservation of Brodiaea filifolia
is dependent on several factors that
include, but are not limited to,
maintenance of areas of sufficient size
and configuration to sustain natural
ecosystem components, functions, and
processes (e.g., full sun exposure,
natural fire and hydrologic regimes,
adequate biotic balance to prevent
excessive herbivory); protection of
existing substrate continuity and
structure, connectivity among groups of
plants within geographic proximity to
facilitate gene flow among the sites
through pollinator activity and seed
dispersal; and sufficient adjacent
suitable habitat for vegetative
reproduction and population expansion.
The areas being designated as critical
habitat provide one or more of the
physical or biological features essential
to the conservation of this species.
Lands designated as critical habitat
for Brodiaea filifolia occur within the
historical range of the species. Based on
the best available scientific information
available regarding the life history,
ecology, and distribution of this species,
we believe that the primary constituent
elements for B. filifolia are:
(1) Appropriate soil series and
associated vegetation at suitable
elevations of either:
(A) Clay soil series of various origins
(e.g., Alo, Altamont, Auld, Diablo), clay
lenses found as unmapped inclusions in
other soils series, or within loamy soils
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underlain by a clay subsoil (e.g.,
Fallbrook, Huerhuero, Las Flores) that
generally occur on mesas and gentle to
moderate slopes, or in association with
vernal pools, between the elevations of
100 ft (30 m) and 2,500 ft (765 m) and
support open native or annual grassland
communities, within open coastal sage
scrub or coastal sage scrub-chaparral
communities; or
(B) Silty loam soil series underlain by
a clay subsoil or caliche that are
generally poorly drained, moderately to
strongly alkaline, granitic in origin (e.g.,
Domino, Grangeville, Waukena,
Willows), that generally occur in lowlying areas and floodplains, often in
association with vernal pool or playa
complexes, between the elevations of
600 ft (180 m) and 1,800 ft (550 m) and
support native, annual, or alkali
grassland or scrub communities; or
(C) Clay loam soil series (e.g.,
Murrieta) underlain by heavy clay loams
or clays derived from olivine basalt lava
flows that generally occur on mesas and
gentle to moderate slopes between the
elevations of 1,700 ft (520 m) and 2,500
ft (765 m) and support native or annual
grassland or oak woodland savannah
communities associated with basalt
vernal pools; or
(D) Sandy loam soils derived from
basalt and granodiorite parent materials,
deposits of gravel, cobble, and boulders,
or hydrologically fractured weathered
granite in intermittent streams and
seeps that support open riparian and
freshwater marsh communities
associated with intermittent drainages,
floodplains, and seeps generally
between 1,800 ft (550 m) and 2,500 ft
(765 m).
(2) Areas with an intact surface and
subsurface structure not permanently
altered by anthropogenic land use
activities (e.g., deep, repetitive disking;
grading). These features as well as
associated physical processes (e.g., full
sunlight exposure) are essential to
maintain those substrate and vegetation
types where Brodiaea filifolia is found
and to support pollinator assemblages
necessary to facilitate gene flow within
and among populations of B. filifolia.
Criteria Used To Identify Critical
Habitat
We delineated critical habitat using
the following criteria: (1) Essential
occurrences; (2) presence of suitable
vegetation; (3) presence of suitable soil
types; and (4) an area about 820 ft (250
m) of vegetation surrounding each
occurrence to provide for pollinator
movement and habitat. We then
evaluated the critical habitat areas to
determine if any areas should be
exempted or excluded from designation
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under sections 4(a)(3) or 4(b)(2) of the
Act.
We defined habitat containing
features essential to the conservation of
the species as areas of intact, occupied
habitat and/or areas necessary to
maintain gene flow, and/or areas
containing significant populations.
In our proposed rule we defined
significant populations supporting 1,000
or more naturally occurring individuals
of Brodiaea filifolia and/or those found
in unique habitat; for example,
populations found within an atypical
vegetative community, on atypical soils,
and/or at an atypical elevation.
Populations found within unique
habitat types may harbor genetic
diversity that facilitates their
persistence in these areas. This overall
diversity may be important to the
conservation of the species.
In this final designation, we defined
significant occurrences as those
containing 850 plants or more. This
threshold of significance was derived
from a review of all known population
estimates in areas proposed for critical
habitat designation. A review of the
population estimates in the proposed
units revealed a significant step between
populations containing 250 or fewer
plants and those supporting 850 or
more. Barrett and Kohn (1991) have
discussed the consequences of small
population size in plants. They stress
the need for maintaining genetic
variability, especially for rare alleles.
Maintaining diversity of selfincompatible alleles is important to
ensure production of fertile seeds and
thus is important for the survival of
smaller populations. The likelihood of
maintaining this diversity is increased
with more individuals. We believe that
occurrences supporting at least 850
plants have the most potential to
contribute to the long-term conservation
of the species.
Often significant populations are also
peripheral populations. Peripheral
populations of a species are separable
by geographical and/or ecological
differences from central populations
(Lesica and Allendorf 1995).
Conservation of species may depend
upon protection of the genetic
variability present across the range of a
species. Reduced gene flow and limited
seed dispersal may contribute to the
genetic diversity of peripheral
populations attributable to genetic drift
from central populations. Population
divergence may also be attributed to
differences in habitat such as soil types,
fire frequency, and climate (Lesica and
Allendorf 1995). Ornduff (1966) found
the highest concentration of
morphological and cytological variants
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at the margin of the geographic range of
species of Lasthenia. For these reasons,
conservation of geographically (e.g., Los
Angeles County) and ecologically (e.g.,
Devil Canyon) peripheral populations
may be essential for the conservation of
B. filifolia.
Currently, the exact number of extant
populations or occurrences of Brodiaea
filifolia is unknown. Reasons for this
include the lack of surveys in all areas
of suitable habitat, false negative survey
results yielded during inappropriate
seasons, and variation in how survey
data is recorded. For example, some
surveyors may record populations
within close proximity as a single
occurrence while others may record
each population as an individual
occurrence. Table 3 of Bramlet and
White (2004) contains a working list of
approximately 83 sites where B. filifolia
has been reported. However, some of
these sites are included with others as
single occurrences by the CNDDB,
others have no locator, no population
description, are translocated
populations, or were considered
extirpated. These sites were not
considered further. Occurrences
comprised solely of translocated plants
were not considered to contain the
features essential to the conservation of
the species because their potential for
long-term survival and contribution to
the species’ gene pool is currently
unknown.
Where possible, we delineated a
vegetative area of 820 ft (250 m) around
each occurrence included in this
designation to provide for pollinator
movement and habitat. One study found
a 50 percent reduction in seed set when
pollinator habitat was 3,280 ft (1,000 m)
from a target plant species and at 820 ft
(250 m) for another target plant species
(Steffan-Dewenter and Tscharntke
1999). Studies also suggest that the
degradation of pollinator habitat is
likely to adversely affect the abundance
of pollinator species (Jennersten 1988;
Rathcke and Jules 1993; SteffanDewenter and Tscharntke 1999). The
various pollinator species associated
with Brodiaea filifolia as well as studies
quantifying insect pollinating flight
distances are discussed in the
‘‘Background’’ section of this rule.
Studies to quantify the distance that
bees will fly to pollinate their host
plants are limited in number, but the
few that exist indicate that some bees
will routinely fly from 328 to 984 ft (100
to 500 m) to pollinate plants with some
flying at least 3,280 ft (1,000 m) to
pollinate flowers (Schulke and Waser
2001; Steffan-Dewenter and Tscharntke
2000). Because we do not currently have
much information on specific visitation
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behavior of the pollinator species
identified on B. filifolia, we based the
820 ft (250 m) distance on a
conservative estimate for mean routine
flight distance for bees. These 820 ft
(250 m) areas contain suitable soils and
vegetation required by all stages of the
species’ lifecycle and provide for gene
flow, pollen dispersal, seed dispersal,
and germination.
When determining critical habitat
boundaries, we made every effort to
avoid the designation of developed land
such as buildings, paved areas, and
other structures that lack PCEs for
Brodiaea filifolia. Any such structures,
and the land under them, inadvertently
left inside the mapped critical habitat
boundaries due to scale have been
excluded by text in the rule and are not
designated as critical habitat. Therefore,
Federal actions limited to these areas
would not trigger section 7
consultations, unless they affect the
species and/or primary constituent
elements in adjacent critical habitat.
Special Management Considerations or
Protection
When designating critical habitat, we
assess whether the identified primary
constituent elements (PCEs) may require
special management considerations or
protection. Threats to the PCEs for
Brodiaea filifolia include the direct and
indirect effects of habitat loss and
degradation from urban development;
invasive plant species; recreational
activities; agricultural practices;
mowing; and dumping of manure and
sewage sludge on suitable habitat.
Loss and degradation of habitat from
development was cited in the final
listing rule as a primary cause for the
decline of Brodiaea filifolia. Most of the
populations of this species are located
in San Diego, Orange, and Riverside
counties. These counties have had and
continue to have increasing populations
and attendant housing pressure. Natural
areas in these counties are frequently
near or bounded by urbanized areas.
Urban development removes the plant
community components and associated
clay soils identified in the primary
constituent elements. This eliminates or
fragments the populations of B. filifolia.
Urbanization may also indirectly alter
surface as well as subsurface layers to
the degree that they will no longer
support plant community types known
to be associated with B. filifolia.
Invasive plant species may alter the
vegetation composition or physical
structure identified in the primary
constituent elements to an extent that
the area does not support B. filifolia or
its associated vegetation and invasive
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73839
species may compete for space and
resources.
Authorized and unauthorized
recreation activities may impact the
vegetation composition and soil
structure to an extent that the area will
no longer have intact soil surfaces or
support associated vegetation as
identified in the primary constituent
elements. Public hiking trails and/or offroad vehicle activity are examples of
this type of activity.
Some methods of mowing and disking
for agricultural or fire management may
preclude the full and natural
development of Brodiaea filifolia by
adversely affecting the primary
constituent elements. Mowing may
reduce the production and dispersal of
seeds, alter the associated vegetation
needed for pollinator activity, or reduce
the number and vigor of plants present
by cutting off the leaves (PCE# 2).
Dumping of sewage sludge can cover
plants as well as the soils they need. In
addition this practice can alter the
chemistry of the substrate and lead to
alterations in the vegetation supported
at the site (PCE# 1).
Several management actions can
preserve the PCEs for Brodiaea filifolia.
Foremost among these is avoidance of
habitat known to be occupied. However,
set-aside areas must usually include
some form of management to address
other threats to the PCEs (e.g., nonnative plant invasion). Loss of habitat or
degradation of soils can be avoided with
appropriate grading and soil
management as part of development.
Slope grading so as to avoid inflow or
outflow of sediments may protect the
integrity of the onsite soils that support
B. filifolia and associated vegetation.
Dumping of sewage sludge should be
avoided in all areas containing B.
filifolia. The components in sludge can
permanently alter the soil chemistry as
well as the vegetation it supports.
Invasive plant species may be
managed by reducing the overgrowth of
these plants through a combination of
clearing, mowing, and/or thatch
removal. Any temporary impacts from
recreational activities could be timed to
avoid the most sensitive time of year
and hydrological conditions for
Brodiaea filifolia. Mowing and disking
for agricultural or fire suppression
purposes could be located in such a
manner so as to avoid known
populations of the species. Habitat
enhancement can allow for additional
habitat for pollinators as well as for B.
filifolia.
Critical Habitat Designation
We are designating 597 ac (242 ha) of
critical habitat within 4 units/subunits
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in Los Angeles and San Diego counties.
Habitat containing features essential to
the conservation of Brodiaea filifolia in
Riverside, Orange, and San Diego
counties covered by approved and/or
pending HCPs, or a Settlement
Agreement has been excluded from this
final designation. Habitat containing
features essential to the conservation of
B. filifolia on Camp Pendleton is exempt
under section 4(a)(3) of the Act (see
‘‘Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the
Act’’ for a detailed discussion). Areas
designated as critical habitat are under
Federal and private ownership. The
species is not currently known to occur
on any Tribal-owned lands within its
range; therefore, no Tribal-owned lands
are included in this designation. Table
2 provides the approximate area of
critical habitat by county and land
ownership. Table 3 provides the
approximate area of areas containing
features essential to the conservation of
the species, areas excluded from the
final designation, and total critical
habitat designated for B. filifolia.
TABLE 2.—LAND OWNERSHIP ACREAGE (ACRES (AC); HECTARES (HA)) AND COUNTY OF UNITS AND SUBUNITS
DESIGNATED AS FINAL CRITICAL HABITAT FOR BRODIAEA FILIFOLIA.
Critical habitat unit & subunit
County
Private
(ac; ha)
*Federal
(ac; ha)
Total
(ac; ha)
Unit 1: Los Angeles County ..............................................................................
1a: Glendora ..............................................................................................
1b: San Dimas ...........................................................................................
Unit 5: Northern San Diego County ..................................................................
5b: Devil Canyon ........................................................................................
Unit 8: San Marcos ...........................................................................................
8d: Upham ..................................................................................................
Los Angeles
......................
......................
San Diego ....
......................
......................
......................
........................
96; 39
178; 72
........................
0
........................
54; 22
........................
0
20; 8
........................
249; 101
........................
0
........................
96;39
198; 80
........................
249; 101
........................
54; 22
Total ....................................................................................................
......................
328; 133
269; 109
597; 242
*Federal lands included in this designation are managed by the Angeles National Forest and the Cleveland National Forest.
TABLE 3.—AREAS CONTAINING FEATURES ESSENTIAL TO THE CONSERVATION OF THE SPECIES, AREAS EXEMPTED OR EXCLUDED FROM THE DESIGNATION, AND TOTAL CRITICAL HABITAT DESIGNATED FOR Brodiaea filifolia IN ACRES (AC)
AND HECTARES (HA)
Please note that discrepancies in totals are due to rounding.
Total habitat
with features
essential to
the conservation of the
species
County
Los Angeles ......................................................................................................................................
San Bernardino ................................................................................................................................
Orange ..............................................................................................................................................
Riverside ...........................................................................................................................................
San Diego .........................................................................................................................................
Total ..........................................................................................................................................
The units described below constitute
our best assessment at this time of those
areas containing features essential to the
conservation of Brodiaea filifolia. Each
unit or subunit contains the PCEs
related to an intact surface and
subsurface structure essential to
maintain the identified soil and
vegetation types where the species is
found, and support for pollinator
assemblages necessary to facilitate gene
flow within and among populations of
B. filifolia. Lands within each unit or
subunit are also currently occupied and
within the historical range of B. filifolia.
Descriptions of each final critical
habitat unit and the reasons why they
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are included in the designation are
listed below. Unit descriptions also
include the size of the unit, the general
vegetation and soil types present in the
unit, any known threats specific to the
unit, and numbers of individual plants,
if known. Because the species may be
present as mature but non-flowering
corms or immature corms rather than
flowering plants, the number of
individuals given should be considered
an estimate of the minimum number of
plants present. In this final rule we have
retained the same unit/subunit
identifiers that we used in the proposed
designation for this species. We believe
the consistent use of one set of unit/
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Habitat exempted/excluded from
the final designation
Designated
critical habitat
294 ac ..........
119 ha ..........
0 ac ..............
0 ha ..............
1,158 ac .......
469 ha ..........
3,062 ac .......
1,239 ha .......
1884 ac ........
762 ha ..........
6,397 ac .......
2589 ha ........
0 ac ..............
0 ha ..............
0 ac ..............
0 ha ..............
1,158 ac .......
469 ha ..........
3,062 ac .......
1,239 ha .......
1580 ac ........
639 ha ..........
5800 ac ........
2,347 ha .......
294 ac.
119 ha.
0 ac.
0 ha.
0 ac.
0 ha.
0 ac.
0 ha.
303 ac.
123 ha.
597 ac.
242 ha.
subunit identifiers allows for easier
comparison between the proposed
critical habitat and final critical habitat
maps.
Unit Descriptions
Unit 1: Los Angeles County Unit—
This unit consists of 294 ac (119 ha)
divided into 2 subunits.
Subunit 1a: Glendora. This subunit,
known to be occupied at the time of
listing, consists of 96 ac (39 ha) of
private lands in the City of Glendora, in
the foothills of the San Gabriel
Mountains, eastern Los Angeles County.
Lands within this subunit contain
Cieneba-Exchequer-Sobrant soils, a type
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of silty loam, and consist primarily of
southern mixed chaparral and coastal
sage scrub. This population represents
only one of two occurrences located in
the foothills of the San Gabriel
Mountains part of the Transverse Range,
where the species was historically
found, and represents the nearest
genetic connection to the San Dimas
subunit. This unit supports a significant
occurrence of about 2,000 Brodiaea
filifolia associated with annual
grassland interstices in mixed chaparral.
This occurrence is also significant
because it is the northernmost known
occurrence of the species. Populations
reported at this site in 1991 represent
the rediscovery of a population last
documented in 1921 (CNDDB 2005).
The site is owned and managed by the
Glendora Community Conservancy
(GCC). Currently, no management plan
has been developed for these lands,
although the GCC has indicated that
they are willing to develop a
management plan for this species on
their property (Ann Croissant, GCC pers.
comm. to G. Wallace USFWS 2005).
Special management considerations
may be required to control invasive
plant species; to maintain the identified
vegetation types as well as pollinator
habitat essential to the conservation of
the species.
Subunit 1b: San Dimas subunit. This
subunit consists of 198 ac (80 ha) of
Federal (Angeles National Forest) and
privately owned lands on the boundary
between the City of Glendora and the
City of San Dimas in the foothills of the
San Gabriel Mountains of eastern Los
Angeles County. Lands within this
subunit contain Cieneba-ExchequerSobrant soils, a type of silty loam, and
consist primarily of coastal sage scrub
and southern mixed chaparral. Lands in
this subunit support two significant
populations totaling about 6,000 plants
associated with interstitial annual
grassland near chaparral (CNDDB 2005).
The occurrences are also significant
because they are peripheral to the range
of the species. This is one of only two
areas in the foothills of the San Gabriel
Mountains of the Transverse Range
where Brodiaea filifolia occurred
historically, and represents the only
likely genetic connection to plants in
the Glendora subunit. While B. filifolia
is not currently known to occur on the
Angeles National Forest, it occurs just
outside the boundary. Approximately 20
ac (8 ha) of Angeles National Forest
lands are included in the designation to
provide for pollinator habitat. The City
of Glendora conducted an appraisal for
a portion of the area for consideration of
acquisition, but no action to acquire the
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property has been taken (D. Walter,
Senior Planner City of Glendora pers.
comm. to G. Wallace USFWS 2005).
This site is threatened by urban
development. The City of Glendora has
reviewed several proposals for
development of this area (D. Walter,
Senior Planner City of Glendora pers.
comm. to G. Wallace USFWS 2005). In
addition, the City of Glendora has
halted illegal grading on a property in
the northern portion of the subunit.
Therefore, special management may be
required to minimize disturbance to the
surface and subsurface structure within
this subunit and to maintain the
identified soil and vegetation types as
well as pollinator habitat essential to the
conservation of the species.
Subunit 5b: Devil Canyon. This
subunit consists of 249 ac (101 ha) of
federally managed land (Cleveland
National Forest) in northeastern San
Diego County. Lands within this subunit
support an occurrence of Brodiaea
filifolia estimated in the thousands
(CNDDB 2005). Although there are some
hybrids of B. filifolia and B. orcuttii in
this subunit, the level of hybridization
is less extensive than in the Miller
Mountain area; therefore, it is likely that
a minimum of 850 plants are pure B.
filifolia. This occurrence is also
significant in that it is found at the
uppermost elevation range within the
geographic area occupied by the species.
This occurrence is found in an
ecologically unique habitat of vernal
seeps and drainages on low granitic
outcrops in chamise chaparral (CNDDB
2005). The Cleveland National Forest
does not currently have a management
plan specific to Brodiaea filifolia,
however, timing of cattle grazing has
been adjusted to avoid the flowering
period for the species (Kirsten Winter,
Forest Botanist, pers. comm. 2004).
Special management may be required to
minimize disturbance to the surface
structure within this subunit, to control
invasive species, and to maintain the
identified vegetation types as well as
pollinator habitat essential to the
conservation of the species.
Subunit 8d: Upham. This subunit
consists of 54 ac (22 ha) of privately
owned land in the City of San Marcos,
northern San Diego County. The subunit
is immediately surrounded by urban
development. However, areas of extant
valley and foothill grasslands exist in
the surrounding area. This occurrence
contained about 1,000 plants in 1986
and again in 1995 (CNDDB 2005). In
addition, the occurrence of Brodiaea
filifolia in this subunit occurs in a
unique habitat in that the plants are in
association with vernal pools. Plants in
this subunit are threatened by urban
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73841
development, and special management
may be required to minimize
disturbance to the surface and
subsurface structure within this subunit
and to maintain the identified soil and
vegetation types.
Effects of Critical Habitat Designation
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. 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. We are currently
reviewing the regulatory definition of
adverse modification in relation to the
conservation of 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 proposed
species or result in destruction or
adverse modification of proposed
critical habitat. Conference reports
provide conservation recommendations
to assist the agency in eliminating
conflicts that may be caused by the
proposed action. We may issue a formal
conference report if requested by a
Federal agency. Formal conference
reports on proposed critical habitat
contain an opinion that is prepared
according to 50 CFR 402.14, as if critical
habitat were designated. We may adopt
the formal conference report 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)). Until such a
time as a proposed designation is
finalized, any reasonable and prudent
alternatives or reasonable and prudent
measures included in a conference
report are advisory.
If a species is listed or critical habitat
is designated, section 7(a)(2) requires
Federal agencies to ensure that activities
they authorize, fund, or carry out are not
likely to jeopardize the continued
existence of such species or destroy or
adversely modify its critical habitat. If a
Federal action may affect a listed
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species or its critical habitat, the
responsible Federal agency (action
agency) must enter into consultation
with us. Through this consultation, the
action agency ensures that their actions
do not destroy or adversely modify
critical habitat.
When we issue a biological opinion
concluding that a project is likely to
result in 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
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 instances where critical
habitat is subsequently designated and
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 or conference with us on
actions for which formal consultation
has been completed, if those actions
may affect designated critical habitat or
adversely modify or destroy proposed
critical habitat.
Federal activities that may affect
Brodiaea filifolia or its critical habitat
will require section 7 consultation.
Activities on non-Federal lands
requiring a permit from a Federal
agency, such as a permit from the U.S.
Army Corps of Engineers under section
404 of the Clean Water Act, a section
10(a)(1)(B) permit from the Service, or
some other Federal action, including
funding (e.g., Federal Highway
Administration or Federal Emergency
Management Agency) will also continue
to be subject to the section 7
consultation requirement. Federal
actions not affecting listed species or
critical habitat and actions on nonFederal and private lands that are not
federally funded, authorized, or
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permitted do not require section 7
consultation.
Each of the areas designated in this
rule has been determined to contain
sufficient PCEs to provide for one or
more of the life history requirements of
B. filifolia. In some cases, the PCEs are
being taken into consideration in
ongoing Federal actions. As a result,
ongoing Federal actions at the time of
designation will be included in the
baseline in any consultation conducted
subsequent to this designation.
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 Brodiaea filifolia. Federal activities
that, when carried out, may adversely
affect critical habitat for B. filifolia
include, but are not limited to:
(1) Removing, thinning, or destroying
Brodiaea filifolia habitat (as defined in
the ‘‘Primary Constituent Elements’’
discussion), whether by burning,
mechanical, chemical, or other means
(e.g., plowing, grubbing, grading,
grazing, woodcutting, construction, road
building, mining, mechanical weed
control, herbicide application, etc.);
(2) Activities that degrade or destroy
Brodiaea filifolia habitat (and its PCEs)
including, but not limited to, livestock
grazing, clearing, disking, farming,
residential or commercial development,
introducing or encouraging the spread
of nonnative species, off-road vehicle
use, and heavy recreational use;
(3) Activities that diminish habitat
value or quality through indirect effects
(e.g., edge effects, invasion of exotic
plants or animals, or fragmentation);
(4) Any activity, including the
regulation of activities by the Corps of
Engineers under section 404 of the
Clean Water Act or activities carried out
by or licensed by the Environmental
Protection Agency (EPA), that could
alter watershed or soil characteristics in
ways that would alter or reduce the
quality or quantity of surface and
subsurface flow of water needed to
maintain Brodiaea filifolia habitat (these
activities include, but are not limited to,
altering the natural fire regime either
through fire suppression or by using
prescribed fires that are too frequent or
poorly timed; development, including
road building and other direct or
indirect activities; and agricultural
activities, livestock grazing, and
vegetation manipulation such as
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clearing or grubbing in the watershed
upslope from B. filifolia);
(5) Road construction and
maintenance, right-of-way designation,
and regulation of agricultural activities,
or any activity funded or carried out by
the Department of Transportation or
Department of Agriculture that could
result in excavation, or mechanized
land clearing of Brodiaea filifolia
habitat; and
(6) Licensing of construction of
communication sites by the Federal
Communications Commission or
funding of construction or development
activities by the U.S. Department of
Housing and Urban Development that
could result in excavation, or
mechanized land clearing of Brodiaea
filifolia habitat.
The 4 critical habitat units are within
the geographical area occupied by the
species and contain the features
essential to the conservation of Brodiaea
filifolia. Additionally, all habitats
within this designation are likely to be
used by the pollinators for the species.
Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the
Act
In our critical habitat designations, we
use the provisions outlined in sections
3(5)(A), 4(a)(3), and 4(b)(2) of the Act to
evaluate those specific areas that we are
considering for critical habitat
designation. Lands that we determined
do not meet the definition of critical
habitat under section 3(5)(A), lands that
have been exempted under section
4(a)(3), and areas excluded under
section 4(b)(2) include those already
receiving special management
considerations or protection, are
covered by legally operative HCPs that
include Brodiaea filifolia as a covered
species, are covered by a INRMP that
was determined to provide a benefit to
the species, or are proposed for coverage
in a draft HCP or other identified
conservation effort for which we have a
reasonable expectation will reach a
successful outcome.
Application of Section 3(5)(A) of the Act
Section 3(5)(A) of the Act defines
critical habitat as the specific areas
within the geographical area occupied
by the species at the time of listing on
which are found those physical or
biological features (I) essential to the
conservation of the species and (II)
which may require special management
considerations or protection. Therefore,
areas within the geographical area
occupied by the species at the time of
listing that do not contain the features
essential for the conservation of the
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species are not, by definition, critical
habitat. Similarly, areas within the
geographical area occupied by the
species at the time of listing containing
essential physical or biological features
that do not require special management
considerations or protection also are
not, by definition, critical habitat. To
determine whether an area requires
special management, we first determine
if the features essential to the
conservation of the species located there
generally require special management to
address applicable threats. If those
features do not require special
management, or if they do in general but
not for the particular area in question
because of the existence of an adequate
management plan or for some other
reason, then the area does not require
special management.
We consider a current plan to provide
adequate management or protection if it
meets two criteria: (1) The plan provides
management, protection or
enhancement to the PCEs at least
equivalent to that provided by a critical
habitat designation; and (2) the Service
has a reasonable expectation that the
management, protection or
enhancement actions will continue for
the foreseeable future.
We are not including habitat
containing features essential to the
conservation of Brodiaea filifolia in
subunit 8b (Rancho Santalina/Loma
Alta) in the City of San Marcos, San
Diego County, California, under section
3(5)(A) of the Act. This subunit is
composed of two properties, Rancho
Santalina and Loma Alta. Rancho
Santalina has completed a long-term
management plan that specifically
addresses B. filifolia. Likewise, the
Loma Alta development has submitted a
Perpetual Habitat Management Plan that
addresses B. filifolia. In determining
whether an area is adequately managed
and does not require special
management, the Service generally
evaluates existing management to
determine whether it provides (1) a
conservation benefit to the species; (2)
reasonable assurances for
implementation; and (3) reasonable
assurances that conservation efforts will
be effective.
The Rancho Santalina project
includes a completed a long-term
management plan in November 2003,
specifically for the long-term protection
and enhancement of Brodiaea filifolia
(Dudek and Associates 2003).
Approximately 1,500 plants on 5.8 acres
will be included in a Preserve Site.
Impacted plants (about 430) from the
site will be translocated to the
contiguous 1 ac (.4 ha) area. Additional
plants will be translocated from the Las
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Posas Road/State Route 78 Interchange
Project. The total acreage of the Preserve
Site is 6.8 acres. The site will be
preserved and managed in perpetuity
with funding provided through a nonwasting endowment of $103,888 (Office
of Administrative Law 2003). The site
will be protected from human and
vehicular access by perimeter fencing
and signage and will be part of the
Northwestern San Diego County
Multiple Habitat Conservation Program
preserve area.
The goals of the management plan are
to preserve the natural population and
translocated plants of Brodiaea filifolia,
and to sustain the coastal sage scrub and
grassland vegetation to support and
buffer the population on site. The site
will be monitored for translocation
success for seven years.
The Loma Alta project has completed
a Perpetual Land Management Plan that
provides a conservation benefit for
Brodiaea filifolia. An area of 0.74 ac (0.3
ha) that has been known to support
approximately 4,000 plants will be
included in the 4.86 acre Loma Alta
Environmental Preserve. A conservation
easement was placed over the Preserve
area in December 2003 (City of San
Marcos 2003). Management provisions
for the site include 12 visits per year to
the site: 9 visits to check for fence
breaks and unauthorized activities, 1
visit to complete vegetation assessments
including the current year’s population
of B. filifolia, 1 visit to remove trash and
exotic species, and 1 visit for a spring
point avian survey.
We found that most of the
management actions proposed in the
two management plans outlined above
would be effective and provide a
conservation benefit for B. filifolia.
Therefore, all of these areas containing
features essential to the conservation of
B. filifolia within the Rancho Santalina/
Loma Alta subunit (8b) are being
removed from consideration in this final
critical habitat designation because
these lands are deemed to be adequately
managed pursuant to section 3(5)(A) of
the Act.
Relationship of Critical Habitat to
Department of Defense Lands
Section 318 of the fiscal year 2004
National Defense Authorization Act
(Pub. L. 108–136) amended the Act by
adding a new section 4(a)(3)(B) to
address the relationship of INRMPs to
critical habitat. This provision prohibits
the Service from designating as critical
habitat any lands or other geographical
areas owned or controlled by the
Department of Defense (DoD), or
designated for its use, that are subject to
an INRMP prepared under section 101
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73843
of the Sikes Act (16 U.S.C. 670a), if the
Secretary determines in writing that
such plan provides a benefit to the
species for which critical habitat is
proposed for designation.
We received comments from the U.S.
Marine Corps regarding the proposed
critical habitat designation, and
economic impact and national security
impact on Department of Defense lands.
We specifically requested information
from the Department of Defense
regarding the benefits of any INRMP to
Brodiaea filifolia in the proposed rule
(69 FR 71284).
Application of Section 4(a)(3) to Camp
Pendleton
In the proposed rule, we excluded
habitat containing features essential to
the conservation of Brodiaea filifolia
within mission-critical training areas on
Camp Pendleton (Camp Pendleton)
under section 4(b)(2) of the Act. In this
final rule, Camp Pendleton is exempt
from critical habitat pursuant to section
4(a)(3) of the Act. Thus, no lands owned
or controlled by Camp Pendleton are
being designated as critical habitat for B.
filifolia.
In November 2001, Camp Pendleton
completed their INRMP (U.S. Marine
Corps 2001), which includes the
following conservation measures for
Brodiaea filifolia: (1) Surveys and
monitoring, studies, impact avoidance
and minimization, and habitat
restoration and enhancement; (2)
species survey information stored in
Camp Pendleton’s GIS database and
recorded in a resource atlas which is
published and updated on a semiannual basis; (3) use of the resource
atlas to plan operations and projects to
avoid impacts to B. filifolia and to
trigger section 7 consultations if an
action may affect the species; and (4)
transplantation when avoidance is not
possible. These measures are
established, ongoing aspects of existing
programs that provide a benefit to B.
filifolia. Camp Pendleton also has Base
directives and Range and Training
Regulations that are integral to their
INRMP, and that provide benefits to B.
filifolia. Camp Pendleton implements
Base directives to avoid and minimize
adverse effects to B. filifolia, such as: (1)
Bivouac, command post, and field
support activities should be no closer
than 164 ft (50 m) to occupied habitat
year round; (2) limiting vehicle and
equipment operations to existing road
and trail networks year round; and (3)
requiring environmental clearance prior
to any soil excavation, filling, or
grading. Camp Pendleton has also
contracted for and funded surveys for B.
filifolia in summer 2005 and a GIS-
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based monitoring system which will
allow them to better manage listed
species on Camp Pendleton, including
B. filifolia.
Camp Pendleton has also
demonstrated ongoing funding of their
INRMP and management of endangered
and threatened species. In Fiscal Year
2002, Camp Pendleton spent
approximately $1.5 million on the
management of federally listed species.
In Fiscal Year 2003, they expended over
$5 million to fund and implement their
INRMP, including management actions
that provided a benefit for Brodiaea
filifolia. Moreover, in partnership with
the Service, Camp Pendleton is funding
two Service biologists to assist in
implementing their Sikes Act program
and buffer lands acquisition initiative.
Based on Camp Pendleton’s past
funding history for listed species and
their Sikes Act program (including the
management of Brodiaea filifolia), there
is a high degree of certainty that Camp
Pendleton will implement their INRMP
in coordination with the Service and the
CDFG in a manner that provides a
benefit to B. filifolia, coupled with a
high degree of certainty that the
conservation efforts of their INRMP will
be effective. Service biologists work
closely with Camp Pendleton on a
variety of endangered and threatened
species issues, including B. filifolia. The
management programs, Base directives,
and Range and Training Regulations to
avoid and minimize impacts to B.
filifolia are consistent with section 7
consultations with Camp Pendleton.
Therefore, the Secretary has found that
the INRMP for Camp Pendleton
provides a benefit for B. filifolia and is
exempting all lands on Camp Pendleton
from critical habitat pursuant to section
4(a)(3) of the Act.
Currently, we are in the process of
completing a programmatic section 7
consultation for upland species on
Camp Pendleton. Brodiaea filifolia is
addressed in this uplands species
consultation. When this consultation is
completed, we anticipate that Camp
Pendleton will incorporate the
conservation measures from the
Biological Opinion into their INRMP. At
that time, Camp Pendleton’s INRMP
will provide further benefits to B.
filifolia.
Relationship of Critical Habitat to
Approved and Pending Habitat
Conservation Plans (HCPs)—Exclusions
Under Section 4(b)(2) of the Act
Section 4(b)(2) of the Act states that
critical habitat shall be designated, and
revised, on the basis of the best
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. An
area may be excluded from critical
habitat if it is determined that the
benefits of exclusion outweigh the
benefits of specifying a particular area
as critical habitat, unless the failure to
designate such area as critical habitat
will result in the extinction of the
species. Consequently, we may exclude
an area from critical habitat based on
economic impacts, impacts on national
security, or other relevant impacts, such
as preservation of conservation
partnerships, if we determine the
benefits of excluding an area from
critical habitat outweigh the benefits of
including the area in critical habitat,
provided the action of excluding the
area will not result in the extinction of
the species.
Under section 4(b)(2) of the Act, we
are excluding critical habitat from
approximately 4,883 ac (1,976 ha) of
non-Federal lands within approved or
pending HCPs. We are excluding nonFederal lands from critical habitat
within the approved (1) Western
Riverside County Multiple Species
Habitat Conservation Plan (MSHCP)
(3062 ac, 1239 ha); (2) Villages of La
Costa Habitat Conservation Plan (HCP)
(208 ac, 84 ha); and (3) Northwestern
San Diego County Multiple Habitat
Conservation Program (MHCP): City of
Carlsbad Subarea Plan/Habitat
Management Plan (City of Carlsbad
HMP) (414 ac, 168 ha). We are also
excluding non-Federal lands from
critical habitat within two pending
HCPs, the (4) City of Oceanside HMP,
also a Subarea Plan under the
Northwestern San Diego County MHCP
(41 ac, 17 ha) and (5) Orange County
Southern Subregion Natural
Communities Conservation Plan
(NCCP)/HCP) (1,158 ac, 468 ha). Table
4 below provides a list of the
exemptions and exclusions in this rule.
We have determined that the benefits of
excluding areas within these legally
operative and pending HCPs from final
critical habitat designation outweigh the
benefits of including them in critical
habitat.
TABLE 4.—ACREAGE OF HABITAT CONTAINING FEATURES ESSENTIAL TO THE CONSERVATION OF THE SPECIES, AREAS EXCLUDED OR EXEMPTED FROM CRITICAL HABITAT, AND DESIGNATED CRITICAL HABITAT (ACRES (AC); HECTARES (HA))
FOR BRODIAEA FILIFOLIA
Total habitat containing features essential to the conservation of Brodiaea filifolia ............................................................................
Habitat excluded from the final critical habitat designation under section 4(b)(2) of the Act:
Western Riverside County Multiple Species Habitat Conservation Plan (Riverside County) .......................................................
Villages of La Costa Habitat Conservation Plan (San Diego County) ..........................................................................................
City of Carlsbad Habitat Management Plan (San Diego County) .................................................................................................
Pending City of Oceanside Subarea Plan (San Diego County) ....................................................................................................
Pending Orange County Southern Subregion Natural Community Conservation Plan/Habitat Conservation Plan (Orange
County).
Habitat exempted from critical habitat designation under section 4(a)(3) of the Act: Marine Corps Base, Camp Pendleton
(San Diego County).
Total habitat containing features essential to the conservation of Brodiaea filifolia excluded or exempted from final critical habitat.
Total habitat containing features essential to the conservation of Brodiaea filifolia designated as final critical habitat .......
Brodiaea filifolia is a covered species
under the approved Western Riverside
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County MSHCP, the Villages of La Costa
HCP, and the City of Carlsbad HMP and,
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6,397 ac.
2,589 ha.
3,062 ac.
1,239 ha.
208 ac.
84 ha.
414 ac.
368 ha.
41 ac.
17 ha.
1,158 ac.
469 ha.
917 ac.
371 ha.
5,800 ac.
2,347 ha.
597 ac.
242 ha.
as such, receives protection and
management of features essential for the
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species’ conservation. We issued the
section 10(a)(1)(B) permit for the
Western Riverside County MSHCP on
June 22, 2005; the Villages of La Costa
HCP on June 7, 1995; and the City of
Carlsbad HMP on November 9, 2004.
Significant conservation of B. filifolia is
also identified and committed to under
a pending HMP for the City of
Oceanside and for the Orange County
Southern Subregion NCCP/HCP through
a signed Settlement Agreement for the
Ranch Plan, a comprehensive land use
and open space plan that is a
component of the draft Orange County
Southern Subregion NCCP/HCP,
addressing lands owned by the County
of Orange and lands owned by Rancho
Mission Viejo. The Settlement
Agreement was signed on August 16,
2005. These approved and legally
operative HCPs, the pending City of
Oceanside HMP, and the pending
Orange County Southern Subregion
NCCP/HCP and associated Settlement
Agreement provide special management
and protection for the physical and
biological features essential for the
conservation of B. filifolia that exceed
the level of regulatory control that
would be afforded this species by the
designation of critical habitat. We have
determined that the benefits of
excluding critical habitat within these
areas from the critical habitat
designation will outweigh the benefits
of including them as critical habitat and
this exclusion will not result in the
extinction of B. filifolia.
Below we first provide general
background information on each
approved or pending HCP, followed by
an analysis pursuant to section 4(b)(2) of
the Act of the benefits of including
lands in all five areas within the critical
habitat designation, an analysis of the
benefits of excluding these lands from
the designation, and an analysis of why
we believe the benefits of exclusion are
greater than the benefits of inclusion.
Finally, we provide a determination that
exclusion of lands within these
approved and pending HCPs will not
result in the extinction of Brodiaea
filifolia.
Western Riverside County Multiple
Species Habitat Conservation Plan
We excluded 3,062 ac (1,239 ha) of
non-Federal lands within the Western
Riverside County MSHCP under section
4(b)(2) of the Act. The Western
Riverside County MSHCP was finalized
and approved on June 22, 2004.
Participants in this HCP include 14
cities; the County of Riverside,
including the Riverside County Flood
Control and Water Conservation
Agency, Riverside County
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Transportation Commission, Riverside
County Parks and Open Space District,
and Riverside County Waste
Department; the California Department
of Parks and Recreation; and
CALTRANS (Riverside County et al.).
The Western Riverside County MSHCP
is a subregional plan under the State’s
NCCP Act of 2001 and was developed
in cooperation with the California
Department of Fish and Game (CDFG).
The Western Riverside County
MSHCP establishes a multiple species
conservation program to minimize and
mitigate the expected loss of habitat
values and, with regard to ‘‘covered’’
animal species, the incidental take of
such species. Within the 1.26-million ac
(510,000 ha) planning area of the
MSHCP, approximately 153,000 ac
(62,000 ha) of diverse habitats are being
conserved. The conservation of 153,000
ac (62,000 ha) complements
approximately 347,000 ac (140,431 ha)
of other existing natural and open space
areas that are already conserved through
other means (e.g., State parks, USFS,
and County park lands). These lands
together will form an overall 500,000-ac
MSHCP Conservation Area.
The MSHCP Plan Area includes a
portion of the range of Brodiaea filifolia,
which is a covered species under this
NCCP/HCP. The Service concluded that
the MSHCP would not jeopardize the
continued existence of B. filifolia in its
Biological and Conference Opinion
(Service 2004).
The MSHCP identifies the following
specific conservation goals that will be
implemented for the long-term
conservation of Brodiaea filifolia: (1) To
include within the MSHCP
Conservation Area at least 6,900 ac
(2,792 ha) of grassland and playa/vernal
pool habitat within the San Jacinto
River, Mystic Lake and Salt Creek areas
that include the 3,062 ac of land that
containing features essential to the
conservation of the species, including
occurrences of B. filifolia identified in
the proposed rule; (2) to include within
the MSHCP Conservation Area at least
11 major locations supporting B. filifolia
in two core areas along the San Jacinto
River and on the Santa Rosa Plateau,
including occurrences identified in the
proposed rule as significant; (3) to
conduct surveys for the species in
certain areas of suitable habitat until the
conservation goals are met; and (4) to
include within the MSHCP
Conservation Area the floodplain along
the San Jacinto River consistent with
objective 1 and to maintain floodplain
processes along the San Jacinto River. In
addition, the MSHCP requires surveys
to be conducted for B. filifolia within
the MSHCP Conservation Area at least
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every 8 years to verify occupancy at a
minimum 75 percent of the known
locations. Management measures will be
triggered, as appropriate, if a decline in
species distribution is documented
below this threshold. Other
management actions will help maintain
habitat and populations of B. filifolia by
preventing alteration of hydrology and
floodplain dynamics, off-road vehicle
use, grazing, and competition from nonnative plants.
Occurrences of Brodiaea filifolia are
frequently associated with or near
vernal pool complexes. The Western
Riverside County MSHCP provides for
special protection of vernal pool
complexes and associated species
through its Protection of Species
Associated with Riparian/Riverine areas
and Vernal Pools policy.
Implementation of this policy will assist
in providing protection to this species’
essential habitat by avoiding and
minimizing direct impacts to vernal
pools and associated habitats. In
addition, B. filifolia is considered an
Additional Survey Needs and
Procedures species under the MSHCP.
Under this policy, surveys for B. filifolia
will be conducted where suitable
habitat is present in identified species
survey areas until such time as the
conservation objectives for this species
are met. Finally, the MSHCP’s
Guidelines Pertaining to the Urban/
Wildlands Interface provides some
assurance that future urbanization will
maintain the existing water quality and
quantity needed to maintain floodplain
areas and vernal pools supporting B.
filifolia along the San Jacinto River and
at upper Salt Creek west of Hemet.
Thus, the Western Riverside County
MSHCP provides significant
conservation benefits to B. filifolia,
including an MSHCP Conservation Area
that protects core habitat areas and
known occurrences, long-term
management and monitoring of the
preserve area, and special guidelines,
policies, and survey requirements to
ensure that significant occurrences of B.
filifolia and its essential habitat are
protected under the plan.
The Villages of La Costa Habitat
Conservation Plan—San Diego County
We excluded 208 ac (84 ha) of nonFederal lands within the Villages of La
Costa HCP under section 4(b)(2) of the
Act. Under this HCP, Fieldstone/La
Costa Associates proposed to construct
housing, limited commercial
development, a school, a park, and
various roadways on 1,252 ac (507 ha)
of the 1,955 ac (791ha) property at two
locations within the City of Carlsbad.
All Brodiaea filifolia on the site
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occurred in the northwest parcel and
was estimated to consist of 7,000
individuals. The project was permitted
to directly impact 1,190 individuals (17
percent). As part of the HCP and section
10(a)(1)(B) permit, the following
conservation measures were required
and have been implemented for the
long-term conservation of B. filifolia: (1)
Permanent protection of approximately
5,800 individuals (83 percent) in a
702.5–ac (284 ha) natural open space
preserve configured to provide
connectivity to other significant areas of
natural habitat; (2) long-term
management of conserved habitat; (3)
monitoring; (4) habitat restoration and
enhancement; (5) control of invasive
plant species; (6) implementation of a
fire management program; (7) access
control measures; and (8) public
education. The 702.5 ac preserve area
contains the significant occurrence of B.
filifolia identified in the proposed rule.
Open space areas on Fieldstone/La
Costa Associates lands are actively
managed to maintain and enhance
biological values by the Center for
Natural Lands Management (Don
Rideout, City of Carlsbad, pers. comm.
2004). In the Service’s 1995 Biological
and Conference opinion for this HCP,
we found that the issuance of the
incidental take permit and execution of
the Implementing Agreement were not
likely to jeopardize the continued
existence of B. filifolia (Service 1995).
We determined that impacts to this
species and its habitat, when viewed in
conjunction with the conservation
measures required under the HCP and
Implementing Agreement that will
provide long-term benefits to B. filifolia,
were not anticipated to result in an
appreciable reduction in the numbers,
reproduction, or distribution of this
species throughout its range.
City of Carlsbad Habitat Management
Plan—San Diego County
We excluded approximately 414 ac
(168 ha) of non-Federal lands within the
City of Carlsbad HMP under section
4(b)(2) of the Act. The City of Carlsbad
HMP is a subarea plan under the
Northwestern San Diego County MHCP.
The MHCP is a comprehensive, multijurisdictional planning program
designed to create, manage, and monitor
an ecosystem preserve in northwestern
San Diego County. 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 North County. The
MHCP includes an approximately
112,000–ac (45,324 ha) study area
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within the cities of Carlsbad, Encinitas,
Escondido, San Marcos, Oceanside,
Vista, and Solana Beach (USFWS and
SANDAG 2003).
The 10(a)(1)(B) permit for the City of
Carlsbad HMP was issued on November
9, 2004, and the City was the first of the
seven participating cities to receive a
permit on their subarea plan. Brodiaea
filifolia is a conditionally covered
species under the HMP. Occurrences of
B. filifolia exist within the boundaries of
the HMP in the following identified
areas: Calavera Heights, Lake Calavera,
Fox-Miller, Carlsbad Oaks North, and
Poinsettia. Under the HMP, all known
populations of B. filifolia within
existing preserve areas will be
conserved at 100 percent. All B. filifolia
outside of already preserved areas are
required to be consistent with the
MHCP’s narrow endemic policy which
requires mitigation for unavoidable
impacts and management practices
designed to achieve no net loss of
narrow endemic populations, occupied
acreage, or population viability within
Focused Planning Areas. 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). All
conserved populations of B. filifolia will
be incorporated into the preserve areas
of the HMP. Additionally, the HMP
includes provisions to manage the
populations within the preserve areas in
order to provide for the long-term
conservation of the species.
Occurrences of Brodiaea filifolia at
Calavera Heights, Lake Calavera,
Carlsbad Oaks North, and Poinsettia
covered under the HMP were excluded
from proposed critical habitat. However,
occurrences on the Fox-Miller property
were not excluded from the proposed
designation because initially, the
proposed hard-lined reserve on FoxMiller did not meet the conditions for
coverage of the species under the HMP.
The property owners worked with the
Service, CDFG, and the City of Carlsbad
to develop a project that meets the
HMP’s standards for B. filifolia
conservation. Ninety-five percent of the
19,100 plants on the property will be
conserved. The site’s preserve will be
incorporated into the HMP’s preserve
system, partially restored to native
grassland, and managed to sustain both
the native grassland community and the
population of B. filifolia. With
modification of this hard-lined reserve
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and associated restoration and
management actions, the City of
Carlsbad will receive full coverage for B.
filifolia. In our biological opinion for the
issuance of the section 10(a)(1)(B)
permit to the City of Carlsbad, we
determined that the proposed action
would not jeopardize the continued
existence of B. filifolia. The preserve
area includes the significant occurrence
of B. filifolia identified in the proposed
rule. Thus, we are excluding the FoxMiller property (subunit 7a) in this final
rule.
City of Oceanside HMP—San Diego
County
We excluded approximately 41 ac (17
ha) of non-Federal lands in two subunits
within the City of Oceanside under
section 4(b)(2) of the Act. The City of
Oceanside has accepted and committed
to the conservation standards for
Brodiaea filifolia established under the
Northwestern San Diego MHCP. These
conservation standards will be included
in the City of Oceanside’s HMP,
currently in development.
Subunit 6b (Mesa Drive) consists of 5
ac (2 ha) of primarily grasslands
supporting an occurrence of Brodiaea
filifolia estimated to contain 2,800
plants (Roberts in litt. 2004). The site is
under the control of a home owner’s
association and includes a San Diego
Gas & Electric utility easement. There
are currently no development plans for
the site, but under the conservation
standards of the overarching,
Northwestern San Diego County MHCP
and agreed to by the City, no more than
20 percent of this population may be
impacted.
Subunit 6d (Taylor/Darwin) contains
several properties under different
ownership. The Taylor Estates property
had 1,268 flowering Brodiaea filifolia
plants identified in 2001. Seventy-one
of these plants in the direct
development footprint of the project
were translocated elsewhere on the
Taylor Estates property. These
translocated individuals and the
remaining plants will be managed and
monitored in perpetuity. The Darwin
portion of the subunit has also been
partially developed. Approximately 6 ac
(2 ha) of open space, which includes an
occurrence of B. filifolia, has been
preserved and will be managed in
perpetuity. Thirty-six ac (15 ha) of
extant valley and foothills grassland
supporting a major population of B.
filifolia, as defined by the MHCP,
remain within the subunit. Under the
conservation standards of the MHCP
and agreed to by the City, 95 percent of
this population will be preserved and
managed within the preserve system.
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The preserve area includes the
significant occurrence of B. filifolia
identified in the proposed rule.
Orange County Southern Subregion
NCCP/HCP
We excluded approximately 1,158 ac
(469 ha) of non-Federal lands in three
subunits within the Southern Subregion
of Orange County under section 4(b)(2)
of the Act.
Rancho Mission Viejo, the County of
Orange, the Endangered Habitats
League, the Natural Resources Defense
Council, Inc., Sea and Sage Audubon
Society, Laguna Greenbelt, Inc., and the
Sierra Club reached an agreement on
August 16, 2005, to settle a lawsuit
challenging the November 2004,
approval for a General Plan
Amendment, Zone Change and
Development Agreement issued by the
County of Orange for Rancho Mission
Viejo’s Ranch Plan, a comprehensive
land use and open space plan for the
remaining 22,815 acres of undeveloped
land owned by Rancho Mission Viejo, in
Orange County. Rancho Mission Viejo’s
Ranch Plan is integral to the pending
Orange County Southern Subregion
NCCP/HCP, currently in development.
We are excluding from critical habitat
designation a total of approximately 899
ac (364 ha) of land owned by Rancho
˜
Mission Viejo in subunits 4c (Canada
Gobernadora/Chiquita Ridgeline) and 4g
(Cristianitos Canyon). Conservation
identified in the Settlement Agreement
assures that significant occurrences of
Brodiaea filifolia will be preserved,
including a major occurrence of over
4,000 plants in subunit 4c. Within
subunit 4c, only small occurrences
(generally less than 100 plants) are
slated for development. Subunit 4g
(Cristianitos Canyon) is primarily
conserved as open space under the
Settlement Agreement. Rancho Mission
Viejo is allowed to establish and
maintain 50 ac (20 ha) of orchards in
this subunit in areas that may impact
some small occurrences of Brodiaea
filifolia. The orchards will be consistent
with the location of, or criteria for
location of, the orchards established by
an approved NCCP or, in the absence of
an approved NCCP, located to avoid
sensitive species and habitats. The
Settlement Agreement also calls for the
establishment of a long-term funding
program for management and oversight
of all defined open space areas placed
under conservation easements.
We are also excluding approximately
259 ac (105 ha) within subunit 4b
(Casper’s Wilderness Park) in the City of
San Juan Capistrano under 4(b)(2) of the
Act. Lands within this unit support an
occurrence of Brodiaea filifolia of about
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850 plants. The occurrence is protected
from urban development and managed
by the County of Orange’s Division of
Harbors, Beaches and Parks. The County
of Orange is a landowner within and a
major sponsor of the Southern
Subregion NCCP/HCP. Thus, the major
occurrences of B. filifolia (i.e., those
with greater than 850 plants)
encompassed within the 1158 acres of
essential habitat identified in the
proposed rule are protected and
included within the planning area
boundary of the draft HCP or committed
for conservation under the Settlement
Agreement.
The following analysis considers all
five plans discussed above: (1) The
Western Riverside County MSHCP; (2)
the Villages of La Costa HCP; (3) the
City of Carlsbad HMP; (4) the City of
Oceanside HMP (pending); and (5) the
Orange County Southern Subregion
NCCP/HCP (pending).
(1) Benefits of Inclusion
Overall, we believe that there is
minimal benefit from designating
critical habitat for Brodiaea filifolia
within the Western Riverside County
MSHCP, the Villages of La Costa HCP,
the City of Carlsbad NCCP/HCP, the City
of Oceanside HMP (pending), and the
Orange County Southern Subregion
NCCP/HCP (pending) because, as
explained above, almost all of the
significant occurrences of B. filifolia are
already protected and managed or will
be protected and managed for the longterm conservation of the species. Below
we discuss benefits of inclusion of these
lands.
A benefit of including an area within
a critical habitat designation is the
protection provided by section 7(a)(2) of
the Act that directs Federal agencies to
ensure that their actions do not result in
the destruction or adverse modification
of critical habitat. The designation of
critical habitat and the analysis to
determine if the proposed Federal
action may result in the destruction or
adverse modification of critical habitat
for Brodiaea filifolia may provide a
different level of protection under
section 7(a)(2) of the Act that is separate
from the obligation of a Federal agency
to ensure that their actions are not likely
to jeopardize the continued existence of
B. filifolia. Under the Gifford Pinchot
decision, critical habitat designations
may provide greater benefits to the
recovery of a species than was
previously believed, but it is not
possible to quantify this benefit at
present. However, the protection
provided under section 7(a)(2) of the
Act is still a limitation on the harm that
occurs to the species or critical habitat
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73847
as opposed to a requirement to provide
a conservation benefit.
The inclusion of these 4,883 ac (1,976
ha) of non-Federal lands as critical
habitat may provide some additional
Federal regulatory benefits for the
species consistent with the conservation
standard based on the Ninth Circuit
Court’s decision in Gifford Pinchot. A
benefit of inclusion would be the
requirement of a Federal agency to
ensure that their actions on these nonFederal lands do not likely result in the
destruction or adverse modification of
critical habitat. This additional analysis
to determine destruction or adverse
modification of critical habitat is likely
to be small because the lands are not
under Federal ownership and any
Federal agency proposing a Federal
action on these 4,883 ac (1,976 ha) of
non-Federal lands would likely consider
the conservation value of these lands as
identified in the approved and pending
HCPs and the Settlement Agreement
and take the necessary steps to avoid
jeopardy or the destruction or adverse
modification of critical habitat.
The areas excluded as critical habitat
include vegetation communities
supporting Brodiaea filifolia and an area
820 ft (250 m) around each occurrence
to provide for pollinator movement and
habitat. If these areas were designated as
critical habitat, any actions with a
Federal nexus, such as the issuance of
a permit under section 404 of the Clean
Water Act, which might adversely affect
the critical habitat would require a
consultation with us, as explained
previously, in the ‘‘Effects of Critical
Habitat Designation’’ section. However,
inasmuch as portions of these areas
currently support B. filifolia,
consultation for Federal activities which
might adversely impact the species
would be required even without the
critical habitat designation. For the
surrounding areas that may lack
individual plants (i.e., areas not
occupied by B. filifolia), the Federal
action agency would need to determine
if the proposed action would affect the
species rather than determining whether
the proposed action would cause
destruction or adverse modification of
critical habitat. A potential benefit of
critical habitat would be to signal the
importance of the surrounding areas not
occupied by B. filifolia to Federal
agencies and to ensure their actions do
not result in the destruction or adverse
modification of critical habitat pursuant
to section 7(a)(2) of the Act. However,
approved and pending HCPs because
almost all of the significant occurrences
of B. filifolia are protected and managed
or will be protected and managed for the
long-term benefit of the species. Thus,
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the approved and draft HCPs provide or
will provide a greater level of protection
and management for B. filifolia than the
simple avoidance of adverse effects to
critical habitat.
If these areas were included as critical
habitat, primary constituent elements
would be protected from destruction or
adverse modification by Federal actions
using a conservation standard based on
the Ninth Circuit Court’s decision in
Gifford Pinchot. This requirement
would be in addition to the requirement
that proposed Federal actions avoid
likely jeopardy to the species’ continued
existence. However, for those areas
supporting Brodiaea filifolia,
consultation for activities which may
adversely affect the species would be
required, even without the critical
habitat designation.
In Sierra Club v. Fish and Wildlife
Service, 245 F.3d 434 (5th Cir. 2001),
the Fifth Circuit Court of Appeals stated
that the identification of habitat
essential to the conservation of the
species can provide informational
benefits to the public, State and local
governments, scientific organizations,
and Federal agencies. The court also
noted that heightened public awareness
of the plight of listed species and their
habitats may facilitate conservation
efforts. The inclusion of an area as
critical habitat may focus and contribute
to conservation efforts by other parties
by clearly delineating areas of high
conservation values for certain species.
However, we believe that this
educational benefit has largely been
achieved for Brodiaea filifolia by the
public outreach and environmental
impact reviews required under the
National Environmental Policy Act
(NEPA) for the Western Riverside
County MSHCP, the Villages of La Costa
HCP, the Northwestern San Diego
County MHCP, and the City of Carlsbad
HMP and the recognition by the County
of Riverside et al., Fieldstone/La Costa
Associates, the City of Carlsbad, the City
of Oceanside, the County of Orange, and
Rancho Mission Viejo of the presence of
B. filifolia and the value of their lands
for the conservation and recovery of the
species. There would be little additional
informational benefit gained from
including these lands as critical habitat
because of the level of information that
has been made available to the public as
part of these regional planning efforts.
Similarly, while the Settlement
Agreement was not open to public
comment, it results from an application
requesting a General Plan Amendment,
Zone Change and Approval of a
Development Agreement that was
subject to extensive public review
through circulation of an Environmental
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Impact Report under CEQA. A major
commitment to the conservation
presented in the Settlement Agreement
has been made public through media
outreach. In addition, the Settlement
Agreement and revisions made to the
Ranch Plan Development Agreement are
now being incorporated into the draft
documents for the Orange County
Southern Subregion NCCP/HCP. The
planning process for this regional
NCCP/HCP has been ongoing for several
years and has included significant
scoping and planning workshops with
opportunity for public comment. The
Settlement Agreement has now
provided the impetus for the County of
Orange, local jurisdictions, and Rancho
Mission Viejo to complete the Southern
Subregion NCCP/HCP. While the Draft
HCP/EIS has not yet been released for
public review, major portions of the
document, including the conservation
analysis sections are complete, and the
Service and the CDFG are coordinating
efforts to review the document. Thus,
the Settlement Agreement and status of
the preliminary Draft HCP/EIS provide
us with reasonable assurance that this
significant regional plan will be
completed.
The pending City of Oceanside HMP
has a similar status to the Orange
County Southern Subregion NCCP/HCP,
in that a conservation strategy for
Brodiaea filifolia has been agreed to and
the planning documents, while not yet
released for public review, are well
underway. In addition, the Oceanside
HMP is a Subarea Plan under the
MHCP, which underwent public review
through a joint CEQA/NEPA process;
based on this, and the cooperation and
efforts of the City of Oceanside to
support the goals of the overarching
MHCP, we have reasonable assurance
that the City of Oceanside HMP will be
completed.
In addition there has been public
notice and opportunity for comment on
this proposal, which identified lands
eligible for designation as critical
habitat, and the economic analysis for
the proposal, which also identified
those lands. Consequently, we believe
that the informational benefits are
already provided even though these
areas are not designated as critical
habitat.
For 30 years prior to the Ninth Circuit
Court’s decision in Gifford Pinchot, the
Fish and Wildlife Service equated the
jeopardy standard with the standard for
destruction or adverse modification of
critical habitat. However, in Gifford
Pinchot the court noted the government,
by simply considering the action’s
survival consequences, was reading the
concept of recovery out of the
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regulation. The court, relying on the
CFR definition of adverse modification,
required the Service to determine
whether recovery was adversely
affected. The Gifford Pinchot decision
arguably made it easier to reach an
‘‘adverse modification’’ finding by
reducing the harm, affecting recovery,
rather than the survival of the species.
However, there is an important
distinction: Section 7(a)(2) limits harm
to the species either through jeopardy or
destruction or adverse modification
analyses. It does not require positive
improvements or enhancement of the
species status. Thus, any management
plan which considers enhancement or
recovery as the management standard
will almost always provide more benefit
than the critical habitat designation.
(2) Benefits of Exclusion
As mentioned above, the Western
Riverside County MSHCP, the Villages
of La Costa HCP, the City of Carlsbad
HMP, the pending City of Oceanside
HMP, and the pending Orange County
Southern Subregion NCCP/HCP and
associated Settlement Agreement
provide for the conservation of Brodiaea
filifolia through avoidance,
minimization, and/or mitigation of
impacts, management of habitat, and
maintenance of watershed. These HCPs
and the Settlement Agreement provide
or will provide for protection of the
PCEs for B. filifolia and address special
management needs such as maintenance
of clay soils and hydrology. Designation
of critical habitat would therefore not
provide as great a benefit to the species
as the positive management measures in
these HCPs and the Settlement
Agreement.
The benefits of excluding lands
within HCPs from critical habitat
designation include relieving
landowners, communities, and counties
of any additional regulatory burden that
might be imposed by a critical habitat
designation consistent with the
conservation standard based on the
Ninth Circuit Court’s decision in Gifford
Pinchot. Many HCPs, particularly large
regional HCPs, such as the Orange
County Southern Subregion NCCP/HCP,
take many years to develop and, upon
completion, become regional
conservation plans that are consistent
with the recovery objectives for listed
species that are covered within the plan
area. Additionally, many of these HCPs
provide conservation benefits to
unlisted, sensitive species. Imposing an
additional regulatory review after an
HCP is completed solely as a result of
the designation of critical habitat may
undermine conservation efforts and
partnerships in many areas. In fact, it
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could result in the loss of species’
benefits if participants abandon the
voluntary HCP process because the
critical habitat designation may result in
additional regulatory requirements than
are faced by other parties who have not
voluntarily participated in species
conservation. Designation of critical
habitat within the boundaries of
approved HCPs could be viewed as a
disincentive to those entities currently
developing HCPs or contemplating them
in the future.
The signed Settlement Agreement
represents a similar commitment to the
conservation of Brodiaea filifolia as
would be found in Draft NCCP/HCP
documents. The Settlement Agreement
is integral to completion of the Orange
County Southern Subregion NCCP/HCP.
We believe designating critical habitat
within the area covered by the signed
Settlement Agreement would be viewed
as a disincentive. Similarly, designating
critical habitat within park lands
designated as wilderness and owned
and managed by the County of Orange,
a major sponsor of the Orange County
Southern Subregion NCCP/HCP, would
be viewed as a disincentive to
completing their regional plan.
Another benefit from excluding these
lands is to maintain the partnerships
developed during the planning phase
through the implementing phases of the
HCPs. Instead of using limited funds to
comply with administrative
consultation and designation
requirements which cannot provide
protection beyond what is currently in
place, the partners could instead use
their limited funds for the conservation
of this species. A related benefit of
excluding lands within HCPs from
critical habitat designation is the
unhindered, continued ability to seek
new partnerships with future HCP
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 HCP plan areas are designated as
critical habitat, it would likely have a
negative effect on our ability to establish
new partnerships to develop HCPs,
particularly large, regional HCPs that
involve numerous participants and
address landscape-level conservation of
species and habitats. By excluding these
lands, we preserve our current
partnerships and encourage additional
conservation actions in the future.
Furthermore, an HCP or NCCP/HCP
application must itself be consulted
upon. While this consultation will not
look specifically at the issue of adverse
modification to critical habitat, unless
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critical habitat has already been
designated within the proposed plan
area, it will determine if the HCP
jeopardizes the species in the plan area.
In addition, Federal actions within the
HCP plan areas that may affect listed
species would still require consultation
under section 7 of the Act. HCPs
typically provide for greater
conservation benefits to a covered
species than section 7 consultations
because HCPs assure the long-term
protection and management of a covered
species and its habitat, and funding for
such management through the standards
found in the 5 Point Policy for HCPs (64
FR 35242) and the HCP ‘‘’No Surprises’’’
regulation (63 FR 8859). Such
assurances are typically not provided by
section 7 consultations that, in contrast
to HCPs, often do not commit the
project proponent to long-term special
management or protections. Thus, a
consultation typically does not accord
the lands it covers the extensive benefits
an HCP provides. The development and
implementation of HCPs provide other
important conservation benefits,
including the development of biological
information to guide the conservation
efforts and assist in species conservation
and the creation of innovative solutions
to conserve species while allowing for
development.
(3) Benefits of Exclusion Outweigh the
Benefits of Inclusion
We have reviewed and evaluated the
exclusion of critical habitat for Brodiaea
filifolia from approximately 4,883 ac
(1,976 ha) of non-Federal lands within
the approved Western Riverside County
MSHCP, the Villages of La Costa HCP,
and the City of Carlsbad HMP, and the
pending City of Oceanside HMP and
pending Orange County Southern
Subregion NCCP/HCP with its
associated Settlement Agreement. Based
on this evaluation, we find that the
benefits of exclusion (avoid increased
regulatory costs which could result from
including those lands in this
designation of critical habitat, ensure
the willingness of existing partners to
continue active conservation measures,
maintain the ability to attract new
partners, and direct limited funding to
conservation actions with partners) of
the lands containing features essential
to the conservation of the Brodiaea
filifolia within these lands outweigh the
benefits of inclusion (limited
educational and regulatory benefits,
which are largely otherwise provided
for under the HCPs) of these lands as
critical habitat. The benefits of
including these 4,883 ac (1,976 ha) of
non-Federal lands as critical habitat are
lessened because of the significant level
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of conservation provided to B. filifolia
under the approved Western Riverside
County MSHCP, the Villages of La Costa
HCP, and the City of Carlsbad HMP; the
pending City of Oceanside HMP; and
the pending Orange County Southern
Subregion NCCP/HCP and associated
Settlement Agreement (conservation of
occupied and potential habitat,
monitoring, and maintenance of soils
and hydrology). In contrast, the benefits
of excluding these 4,883 ac (1,976 ha) of
non-Federal lands as critical habitat are
increased because of the high level of
cooperation by the County of Riverside
et al., Fieldstone/La Costa Associates,
the City of Carlsbad, the City of
Oceanside, the County of Orange,
Rancho Mission Viejo, the State of
California, and the Service to conserve
this species, and these partnerships
exceed any conservation value provided
by a critical habitat designation.
(4) Exclusion Will Not Result in
Extinction of the Species
We believe that exclusion of these
4,883 ac (1,976 ha) of non-Federal lands
will not result in extinction of Brodiaea
filifolia since most of these lands are
protected and managed or will be
protected and managed for the benefit of
this species pursuant to the approved
Western Riverside County MSHCP, the
Villages of La Costa HCP, and the City
of Carlsbad HMP; the pending City of
Oceanside HMP; and the pending
Orange County Southern Subregion
NCCP/HCP and the associated
Settlement Agreement. These approved
and pending HCPs and the Settlement
Agreement include specific
conservation objectives, avoidance and
minimization measures, and
management that exceed any
conservation value provided as a result
of a critical habitat designation.
Some small occurrences of Brodiaea
filifolia within approximately 311 ac
(ha) of privately owned lands in subunit
4c (Gobernadora/Chiquita Ridgeline) are
proposed for development as part of
Rancho Mission Viejo’s development
plan. These lands are covered by the
signed Settlement Agreement. Any
Federal Agency authorizing an action to
develop these lands (e.g., USCOE)
would likely consider the conservation
actions in the Settlement Agreement as
appropriate mitigation for loss of B.
filifolia habitat. We believe the loss of
these small occurrences of this species
is not likely to result in extinction of the
species). Likewise, the approximately
588 acres (238 ha) of privately owned
lands containing features essential to
the conservation of B. filifolia in subunit
4g (Cristianitos Canyon) will be
protected and managed by Rancho
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Mission Viejo as stipulated in the
Settlement Agreement. This level of
protection will occur as a result of the
Settlement Agreement and thus
regardless of whether these lands are
excluded as critical habitat. The
occurrence of B. filifolia in subunit 4b
(Casper’s Wilderness Park) is protected
and is within the pending Orange
County Southern Subregion NCCP/HCP
plan boundary. Thus, we believe that
exclusion of this occurrence as critical
habitat will not result in extinction of
the species.
In our Biological and Conference
Opinions for the issuance of a section
10(a)(1)(B) permit for the Western
Riverside County MSHCP, the Villages
of La Costa HCP, and the City of
Carlsbad HMP, the Service concluded
that the proposed permit issuances
would not appreciably reduce the
likelihood of the survival and recovery
of Brodiaea filifolia because of the
avoidance and minimization measures,
long-term management, and
commitment to a preserve system. The
jeopardy standard of section 7 and
routine implementation of habitat
conservation through the section 7
process also provide assurances that the
species will not go extinct. The
exclusion leaves these protections
unchanged from those that would exist
if the excluded areas were designated as
critical habitat. Critical habitat is being
designated for B. filifolia in other areas
that will be accorded the protection
from adverse modification by Federal
actions using the conservation standard
based on the Ninth Circuit Court’s
decision in Gifford Pinchot.
Additionally, the major occurrences
of Brodiaea filifolia within the Western
Riverside County MSHCP, the Villages
of La Costa HCP, the City of Carlsbad
HMP, and the pending Oceanside HMP
and within lands covered by the
Settlement Agreement and within
Casper’s Wilderness Park are or will be
protected and managed either explicitly
for the species or indirectly through
more general objectives to protect
natural values. These factors, acting in
concert with the other protections
provided under the Act, lead us to find
that exclusion of these 4,883 ac (1,976
ha) within lands owned by the County
of Orange and Rancho Mission Viejo
and within the Western Riverside
County MSHCP, the Villages of La Costa
HCP, the City of Carlsbad HMP, and the
pending City of Oceanside HMP will not
result in extinction of B. filifolia.
Economic Analysis
Section 4(b)(2) of the Act requires us
to designate critical habitat on the basis
of the best scientific data available and
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to consider the economic and other
relevant impacts of designating a
particular area as critical habitat. We
may exclude areas from critical habitat
upon a determination that the benefits
of such exclusions outweigh the benefits
of specifying such areas as critical
habitat. We cannot exclude such areas
from critical habitat when such
exclusion will result in the extinction of
the species concerned.
Following publication of the proposed
critical habitat rule, an analysis of the
economic impacts of proposed critical
habitat for Brodiaea filifolia was
prepared. The notice of availability
(NOA) of a draft economic analysis
(DEA) was announced in the Federal
Register on October 6, 2005 (70 FR
58361). Copies of the draft economic
analysis were available for downloading
from the Internet at https://
carlsbad.fws.gov, or by contacting the
Carlsbad Fish and Wildlife Office
directly. In the NOA, we announced the
reopening of the comment period on
proposed critical habitat and solicited
public review and comment. We
accepted comments until October 20,
2005.
The primary purpose of the economic
analysis is to estimate the potential
economic impacts associated with the
designation of critical habitat for
Brodiaea filifolia. This information is
intended to assist the Secretary in
making decisions about whether the
benefits of excluding particular areas
from the designation outweigh the
benefits of including those areas in the
designation. The economic analysis
considers the economic efficiency
effects that may result from the
designation, including habitat
protections that may be coextensive
with the listing of the species. It also
addresses distribution of impacts,
including an assessment of the potential
effects on small entities and the energy
industry. This information can be used
by the Secretary to assess whether the
effects of the designation might unduly
burden a particular group or economic
sector.
This analysis determined that costs
involving conservation measures for
Brodiaea filifolia would be incurred for
activities involving residential,
industrial, and commercial
development; water supply; flood
control; transportation; agriculture; the
development of HCPs; and the
management of military bases, other
Federal lands, and other public or
conservation lands.
Pre-designation costs include those
Brodiaea filifolia-related conservation
activities associated with sections 4, 7,
and 10 of the Act that have accrued
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since the time that Brodiaea filifolia was
listed as threatened (63 FR 54975;
October 13, 1998), but prior to the
designation of critical habitat. Total predesignation costs associated with lands
proposed as critical habitat are
estimated to be $2.9 million to $3.0
million on a present value basis and
$2.4 million to $2.5 million expressed
in undiscounted dollars. Predesignation costs associated with areas
excluded from the proposed designation
are estimated to be $110,000 to $180,000
on a present value basis and $100,000
to $150,000 expressed in undiscounted
dollars.
Post-designation effects would
include likely future costs associated
with Brodiaea filifolia conservation
efforts in the 20-year period following
the final designation of critical habitat
(effectively 2005 through 2024). If
critical habitat were designated as
proposed, total costs were estimated to
be $12.2 million to $14.7 million on a
present value basis and $12.2 million to
$16.9 million expressed in
undiscounted dollars (an annualized
cost of $0.6 to $0.8 million annually). If
all habitat with features essential to the
conservation of the species were
designated critical habitat in this final
rule, total costs would be expected to
range between $24.5 and $43.6 million
over the next 20 years (an annualized
cost of $1.2 to $2.2 million). However,
due to significant reductions made to
critical habitat in this final rule (see
‘‘Summary of Changes from Proposed
Rule’’), the estimated costs for the units
actually designated are estimated to
range between $1.0 and $3.3 million
over the next 20 years expressed in
undiscounted dollars.
The final economic analysis and
supporting documents are included in
our administrative record and may be
obtained by contacting U.S. Fish and
Wildlife Service, Branch of Endangered
Species (see ADDRESSES section) or for
downloading from the Internet at
https://carlsbad.fws.gov.
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. However, because the
draft economic analysis indicates the
potential economic impact associated
with a designation of all habitat with
features essential to the conservation of
this species would total no more than
$24.5 million to $43.6 million over the
nest 20 years (an annualized cost of $1.2
million to $2.2 million), we do not
anticipate that this final rule will have
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an annual effect on the economy of $100
million or more or affect the economy
in a material way. Due to the time line
for publication in the Federal Register,
the Office of Management and Budget
(OMB) did not formally review the
proposed rule.
The availability of the draft economic
analysis was announced in the Federal
Register on October 6, 2005 (70 FR
58361), and was made available for
public review and comment.
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.
According to the Small Business
Administration (SBA), small entities
include small organizations, such as
independent nonprofit organizations,
and small governmental jurisdictions,
including school boards and city and
town governments that serve fewer than
50,000 residents, as well as small
businesses (13 CFR 121.201). Small
businesses include manufacturing and
mining concerns with fewer than 500
employees, wholesale trade entities
with fewer than 100 employees, retail
and service businesses with less than $5
million in annual sales, general and
heavy construction businesses with less
than $27.5 million in annual business,
special trade contractors doing less than
$11.5 million in annual business, and
agricultural businesses with annual
sales less than $750,000. To determine
if potential economic impacts to these
small entities are significant, we
considered the types of activities that
might trigger regulatory impacts under
this designation as well as types of
project modifications that may result. In
general, the term significant economic
impact is meant to apply to a typical
small business firm’s business
operations.
To determine if this rule to designate
critical habitat for Brodiaea filifolia
would affect a substantial number of
small entities, we considered the
number of small entities affected within
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particular types of economic activities
(e.g., residential, industrial, and
commercial development). We
considered each industry or category
individually to determine if certification
is appropriate. In estimating the
numbers of small entities potentially
affected, we also considered whether
their activities have any Federal
involvement; some kinds of activities
are unlikely to have any Federal
involvement and so will not be affected
by the designation of critical habitat.
Designation of critical habitat only
affects activities conducted, funded,
permitted, or authorized by Federal
agencies; non-Federal activities are not
affected by the designation.
The designation of critical habitat
requires Federal agencies to consult
with us if activities they authorize,
fund, or carry out may affect designated
critical habitat. Consultations to avoid
the destruction or adverse modification
of critical habitat would be incorporated
into the existing consultation process.
Our analysis determined that costs
involving conservation measures for
Brodiaea filifolia would be incurred for
activities involving residential,
industrial, and commercial
development; water supply; flood
control; transportation; agriculture; the
development of HCPs; and the
management of military bases, other
Federal lands, and other public or
conservation lands.
In our draft economic analysis of this
designation, we evaluated the potential
economic effects on small business
entities resulting from conservation
actions related to the listing of this
species and proposed designation of its
critical habitat. Of these potentially
affected activities, impacts to small
entities are not anticipated for the
following reasons: 1. Military lands
management: The analysis predicts that
the Department of Defense (DoD), which
manages Marine Corps Base Camp
Pendleton (EH units 15 to 19), will
experience administrative and project
modification costs associated with
Brodiaea filifolia conservation activities.
DoD does not meet SBA’s definition of
a small government. 2. Transportation,
utilities, and flood control: The analysis
estimates that additional project
modification costs associated with B.
filifolia conservation activities are likely
for transportation project undertaken by
CALTRANS, the Transportation
Corridor Agencies (TCA), and the
Riverside County Transportation
Commission, utility projects undertaken
by San Diego Gas & Electric, and the San
Jacinto River Flood Control Project of
the Riverside County Flood Control and
Water Conservation District. None of
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these five entities are small businesses
or governments as defined by SBA and,
therefore, are not considered further in
this screening analysis. 3. Public and
conservancy lands management: The
United States Forest Service manages
Cleveland National Forest; Orange
County’s Department of Harbors,
Beaches and Parks manages Aliso-Wood
Canyon Regional Park and Casper’s
Regional Park; and the Glendora
Community Conservancy manages the
Conservancy of the same name. With
the exception of the Glendora
Community Conservancy, these entities
exceed the threshold established for
small governments (service population
of 50,000 or less). Accordingly, this
screening analysis focuses on economic
impacts related to residential
development and the management of
Glendora Community Conservancy.
The final critical habitat designation
is expected to result in additional costs
to real estate development projects due
to mitigation and other conservation
costs that may be required. The affected
land is located within Los Angeles,
Orange, and San Diego counties and
under private ownership by individuals
who will either undertake a
development project on their own or
sell the land to developers for
development. For businesses involved
with land development, the relevant
threshold for ‘‘small’’ is annual
revenues of $6 million or less. The
North American Industry Classification
System (NAICS) code 237210 is
comprised of establishments primarily
engaged in servicing land (e.g.,
excavation, installing roads and
utilities) and subdividing real property
into lots for subsequent sale to builders.
Land subdivision precedes actual
construction, and typically includes
residential properties, but may also
include industrial and commercial
properties.
The DEA (See Section 3.2.1) estimates
that 390 acres within areas originally
proposed for critical habitat designation
are projected to be developed over the
next 20 years. The analysis assumes that
as a result of Brodiaea filifolia
conservation activities, 95 percent of the
acres are conserved, and the plant is
salvaged from the remaining five
percent. As a result, landowners of 100
percent of these acres bear costs of B.
filifolia conservation activities.
To estimate the number of
landowners potentially impacted by B.
filifolia conservation activities, the
analysis estimates the average parcel
size within proposed units/subunits in
each county that contains habitat with
features essential to the conservation of
the species and compares it to the
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estimate of affected acres in these areas.
At the aggregate county level, in units
proposed for inclusion, one individual
may be impacted in Los Angeles
County, one individual may be
impacted in San Bernardino County, 22
individuals may be impacted in Orange
County, and 27 individuals may be
impacted in San Diego County. Note
that this estimate may be understated if
habitat partially overlaps several parcels
or overstated if one person owns more
than one parcel with B. filifolia.
The loss in land value experienced by
an individual landowner will depend
on how much of a parcel is inhabited by
Brodiaea filifolia, the extent to which
development activities can be planned
around sensitive areas, and the
existence of alternative uses of the
property that do not threaten the plant
or its habitat. For example, if B. filifolia
exist on only a small portion of the
parcel that can be incorporated into
existing open space requirements, then
a small percentage of the land value is
lost. However, if B. filifolia are found
throughout the parcel, most or all of
development value of that parcel may be
lost. In such a circumstance, the parcel
may continue to derive value from
other, nondevelopment-oriented uses.
Effects on Homebuyers and Small
Construction Firms
The DEA (See Section 3.2.2) estimates
a potential shift in the supply of
housing resulting from increased land
scarcity. Scenario Two assumes that as
a result of on-site conservation
requirements, less land is available for
development, and therefore fewer new
homes are built. Under this scenario,
small construction firms may be
indirectly affected. This analysis uses a
methodology used by Charles River
Associates (CRA) to estimate the
potential impact to small construction
firms. The analysis uses the following
steps to estimate the number of firms
potentially affected:
(1) The analysis estimates the number
of new homes typically built by a small
construction firm in one year. Average
annual revenues for a small
construction firms are $694,000. Using
the average construction costs for a
single family home of $236,000 obtained
from CRA’s vernal pool analysis, a small
firm is assumed to build on average
three houses a year ($694,000/$236,000
= 2.9).
(2) Next, the analysis estimates the
number of homes that would have been
built by small businesses in the absence
of Brodiaea filifolia conservation efforts.
As described in Section 3.2.2 of the
DEA, the analysis predicts 316 homes
will not be built in cities with habitat
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proposed for designation (summarized
in Exhibit A–2 of the DEA). In an
analysis of building permits in
Sacramento County conducted by CRA,
researchers determined that 22 percent
of permits for single family dwellings
were requested by small businesses.
This analysis assumes that a similar
proportion of new home construction
activity is conducted by small
construction firms in the five Southern
California counties included in this
analysis. As shown in Exhibit A–2 of
the DEA, multiplying 22 percent by the
number of homes not built in each
county provides an estimate of lost
home construction for small firms.
(3) Next, using the number of homes
not built by small firms, the analysis
estimates the number of small
businesses affected. Results of this
calculation are presented in Exhibit
A–2. At the high-end, assuming that
each lost house would have been built
by a separate firm, the number of firms
potentially affected is equal to the
number of lost homes. For a low-end
estimate, the number of houses not built
is divided by the average number of
houses built per year by small firms
(three houses). In summary, in a given
municipality containing critical habitat,
between one and 18 small construction
firms may be affected annually by
Brodiaea filifolia conservation activities.
In Hemet, Moreno Valley, and Perris,
where habitat is excluded from critical
habitat, approximately nine to 82 small
firms could be affected if habitat were
designated. The impact to affected small
businesses is estimated to be between
one-third and all of their revenues for
the year, depending on the estimate of
the number of businesses affected. Note
that the impact to small construction
firms may be overstated. As discussed
in Section 3 of the DEA, the analysis of
lost housing units is partial equilibrium
in nature (e.g., does not consider
substitution of displaced development
to other nearby areas), which is
consistent with the best currently
available empirical information. If,
instead, homes not built in these
municipalities are constructed in
neighboring communities unaffected by
B. filifolia conservation activities, the
impact to small construction firms is
likely to be less than presented in
Exhibit A–2. As a result, impacts to
these firms are more likely overstated
than understated in this analysis.
Based on these data, we have
determined that this designation will
not result in a significant economic
impact on a substantial number of small
entities, in particular to land developers
or farmers in Los Angeles, San
Bernardino, Orange, Riverside, and San
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Diego counties. Please refer to Appendix
A of our draft economic analysis of this
designation for a more detailed
discussion of potential economic
impacts to small business entities.
Executive Order 13211
On May 18, 2001, the President issued
Executive Order (E.O.) 13211 on
regulations that significantly affect
energy supply, distribution, and use.
E.O. 13211 requires agencies to prepare
Statements of Energy Effects when
undertaking certain actions. This rule is
considered a significant regulatory
action under E.O. 12866 because it
raises novel legal and policy issues, but
it is not expected to significantly affect
energy supplies, distribution, or use.
Therefore, this action is not a significant
action, and no Statement of Energy
Effects is required. Please refer to
Appendix A of our draft economic
analysis of the proposed designation for
a more detailed discussion of potential
effects on energy supply.
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 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
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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. Non-Federal
entities that receive Federal funding,
assistance, permits, or otherwise require
approval or authorization from a Federal
agency for an action, may be indirectly
impacted by the designation of critical
habitat. However, the legally binding
duty to avoid destruction or adverse
modification of critical habitat rests
squarely on the Federal agency.
Furthermore, to the extent that nonFederal 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) The U.S. Forest Service manages
Angeles National Forest and Cleveland
National Forest (subunits 1b, 5a and 5b);
Orange County’s Department of Harbors,
Beaches and Parks manages Aliso and
Woods Canyon Regional Park (unit 3)
and Casper Wilderness Park (unit 4);
and the Glendora Community
Conservancy manages the Conservancy
(subunit 1a) of the same name. With the
exception of the Glendora Community
Conservancy, these entities exceed the
threshold established for small
governments (service population of
50,000 or less). Therefore, the Glendora
Community Conservancy is the only
land manager considered in this
screening analysis.
The DEA (See Section 6) estimates
potential costs to public and private
land management entities. Of the
entities analyzed, the Glendora
Community Conservancy is the only
small entity. This section estimates
potential impacts of Brodiaea filifolia
conservation activities to the
Conservancy.
The Conservancy’s overall annual
budget ranges from $15,000 to $30,000
and includes such elements as
insurance, discounted land taxes, weed
abatement, and trail maintenance. The
analysis estimates that potential future
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costs associated with Brodiaea filifolia
conservation activities at the
Conservancy may range from $1,600 to
$2,600 on an annualized basis
(assuming a seven percent discount
rate). These costs represent
approximately 11 percent to 17 percent
of annual expenditures assuming the
low-end estimate of the annual budget
($15,000) and 5 percent to 9 percent
assuming the high-end estimate
($30,000). Considering that the Glendora
Community Conservancy is in the
business of conservation this is not an
unexpected expenditure for the
Conservancy. Consequently, we do not
believe that the designation of critical
habitat for B. filifolia will significantly
or uniquely affect any small
governmental entity addressed in the
DEA. As such, a Small Government
Agency Plan is not required.
Federalism
In accordance with Executive Order
13132, this rule does not have
significant Federalism effects and,
therefore, a Federalism assessment is
not required. In keeping with
Department of the Interior policies, we
requested information from, and
coordinated the development of the
proposed critical habitat designation
with appropriate State resource agencies
in California. We anticipate that the
designation of critical habitat in the
areas currently occupied by Brodiaea
filifolia will impose no additional
significant restrictions beyond those
currently in place and, therefore, should
have little incremental impact on State
and local governments and their
activities.
The designation of critical habitat
may have some benefit to the State and
local resource agencies in that the areas
and features essential to the
conservation of this species are more
clearly defined, and the primary
constituent elements of the habitat
necessary to the conservation of this
species are specifically identified. While
this definition and identification does
not alter where and what federally
sponsored activities may occur, it may
assist local governments in long-range
planning (rather than waiting for caseby-case section 7 consultations to
occur).
Civil Justice Reform
In accordance with Executive Order
12988, the Department of the Interior=s
Office of the Solicitor has determined
that this rule does not unduly burden
the judicial system and does meet the
requirements of sections 3(a) and 3(b)(2)
of the Order. We are designating critical
habitat in accordance with provisions of
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73853
the Endangered Species Act. The 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 Brodiaea filifolia.
Paperwork Reduction Act of 1995 (44
U.S.C. 3501 et seq.)
This rule does not contain new or
revised information collections for
which OMB approval is required under
the Paperwork Reduction Act.
Information collections associated with
certain Act permits are covered by an
existing OMB approval and are assigned
OMB Control No. 1018–0094, which
expires September 30, 2007. This
includes FWS Forms 3–200–55 and 3–
200–56. This rule will not impose
recordkeeping or reporting requirements
on State or local governments,
individuals, businesses, or
organizations. An agency may not
conduct or sponsor, and a person is not
required to respond to, a collection of
information unless it displays a
currently valid OMB control number.
National Environmental Policy Act
It is our position that, outside the
Tenth Circuit, we do not need to
prepare environmental analyses as
defined by the NEPA in connection with
designating critical habitat under the
Endangered Species Act of 1973, as
amended. We published a notice
outlining our reasons for this
determination in the Federal Register
on October 25, 1983 (48 FR 49244). This
assertion was upheld in the courts of the
Ninth Circuit (Douglas County v.
Babbitt, 48 F.3d 1495 (9th Cir. Ore.
1995), cert. denied 116 S. Ct. 698
(1996)).
Government-to-Government
Relationship With Tribes
In accordance with the President’s
memorandum of April 29, 1994,
‘‘Government-to-Government Relations
with Native American Tribal
Governments’’ (59 FR 22951), Executive
Order 13175, and the Department of the
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 essential for the conservation of
Brodiaea filifolia. Therefore, critical
habitat has not been designated on
Tribal lands.
References Cited
A complete list of all references cited
herein is available, upon request, from
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the Field Supervisor, Carlsbad Fish and
Wildlife Office (see ADDRESSES section).
Author
Regulation Promulgation
This rule was prepared by staff at the
Carlsbad Fish and Wildlife Office (see
ADDRESSES section).
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.
recordkeeping requirements,
Transportation.
I
List of Subjects in 50 CFR part 17
Accordingly, the Service hereby
amends part 17, subchapter B of chapter
I, title 50 of the Code of Federal
Regulations, as set forth below:
§ 17.12
PART 17—[AMENDED]
Endangered and threatened species,
Exports, Imports, Reporting and
2. In § 17.12(h), revise the entry in the
table for ‘‘Brodiaea filifolia’’ under
‘‘FLOWERING PLANTS,’’ to read as
follows:
I
*
1. The authority citation for part 17
continues to read as follows:
I
Endangered and threatened plants.
*
*
(h) * * *
*
Species
Historic range
Scientific name
Family
Status
*
U.S.A. (CA) .............
*
Liliaceae—Lily ........
When listed
Common names
*
Critical
habitat
Special
rules
FLOWERING PLANTS
*
Brodiaea filifolia .......
*
*
Thread-leaved
brodiaea.
*
*
3. In § 17.96(a), add critical habitat for
Brodiaea filifolia, in alphabetical order
under Family Liliaceae to read as
follows:
I
§ 17.96
Critical habitat—plants.
(a) Flowering plants.
*
*
*
*
*
Family Liliaceae: Brodiaea filifolia
(Thread-leaved brodiaea)
(1) Critical habitat units are depicted
for Brodiaea filifolia on the maps below.
(2) The primary constituent elements
of critical habitat for Brodiaea filifolia
consist of the following:
(i) Appropriate soil series and
associated vegetation at suitable
elevations of either:
(A) Clay soil series of various origins
(e.g., Alo, Altamont, Auld, Diablo), clay
lenses found as unmapped inclusions in
other soil series, or within loamy soils
underlain by a clay subsoil (e.g.,
Fallbrook, Huerhuero, Las Flores) that
generally occur on mesas and gentle to
moderate slopes, or in association with
vernal pools, between the elevations of
100 ft (30 m) and 2,500 ft (765 m) and
support open native or annual grassland
communities, open coastal sage scrub or
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*
650
*
*
*
T
*
coastal sage scrub-chaparral
communities; or
(B) Silty loam soil series underlain by
a clay subsoil or caliche that are
generally poorly drained, moderately to
strongly alkaline, granitic in origin (e.g.,
Domino, Grangeville, Waukena,
Willows), that generally occur in lowlying areas and floodplains, often in
association with vernal pool or playa
complexes, between the elevations of
600 ft (180 m) and 1,800 ft (550 m) and
support native, annual, or alkali
grassland or scrub communities; or
(C) Clay loam soil series (e.g.,
Murrieta) underlain by heavy clay loams
or clays derived from olivine basalt lava
flows, that generally occur on mesas and
gentle to moderate slopes between the
elevations of 1,700 ft (520 m) and 2,500
ft (765 m) and support native or annual
grassland or oak woodland savannah
communities associated with basalt
vernal pools; or
(D) Sandy loam soils derived from
basalt and granodiorite parent materials,
deposits of gravel, cobble, and boulders,
or hydrologically fractured weathered
granite in intermittent streams and
seeps that support open riparian and
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*
17.96(a)
NA.
*
freshwater marsh communities
associated with intermittent drainages,
floodplains, and seeps generally
between 1,800 ft (550 m) and 2,500 ft
(765 m).
(ii) Areas with an intact surface and
subsurface structure not permanently
altered by anthropogenic land use
activities (e.g., deep, repetitive disking;
grading). These features as well as
associated physical processes (e.g., full
sunlight exposure) are essential to
maintain those substrate and vegetation
types where Brodiaea filifolia is found
and to support pollinator assemblages
necessary to facilitate gene flow within
and among populations of B. filifolia.
(iii) Critical habitat does not include
existing features and structures, and the
land beneath them, such as open water,
buildings, roads, aqueducts, railroads,
airport runways and buildings, other
paved areas, lawns, and other urban
landscaped areas not containing one or
more of the primary constituent
elements.
(3) Index map of critical habitat units
for Brodiaea filifolia (Thread-leaved
brodiaea) follows:
BILLING CODE 4310–55–P
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73856
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(4) All map units are in the Universal
Transverse Mercator (UTM) coordinate
system, North American Datum of 1927
(NAD27) projection.
(5) Map Unit 1: Los Angeles, County,
California, from USGS 1:24,000
quadrangle map Glendora California.
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(i) Subunit 1a: Glendora, Los Angeles
County, California; land bounded by the
following UTM coordinates (E, N):
422400, 3779900; 422400, 3779800;
422500, 3779800; 422500, 3779700;
422600, 3779700; 422600, 3779300;
422400, 3779300; 422400, 3779200;
422100, 3779200; 422100, 3779300;
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422000, 3779300; 422000, 3779500;
421900, 3779500; 421900, 3779800;
422000, 3779800; 422000, 3779900;
returning to 422400, 3779900.
(ii) Map of critical habitat Subunit 1a
for Brodiaea filifolia (Thread-leaved
brodiaea) follows:
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73858
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(iii) Subunit 1b: San Dimas; land
bounded by the following UTM
coordinates (E, N): 425300, 3778600;
425300, 3778500; 425400, 3778500;
425400, 3778400; 425500, 3778400;
425500, 3777900; 425400, 3777900;
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425400, 3777800; 425300, 3777800;
425300, 3777700; 425200, 3777700;
425200, 3777500; 424700, 3777500;
424700, 3777600; 424600, 3777600;
424600, 3778200; 424700, 3778200;
424700, 3778500; 424900, 3778500;
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424900, 3778600; returning to 425300,
3778600.
(iv) Map of critical habitat Subunit 1b
for Brodiaea filifolia (Thread-leaved
brodiaea) follows:
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(6) Map Unit 5: Northern San Diego
County, California, from USGS 1:24,000
quadrangle maps Margarita Peak, and
Fallbrook, California.
(i) Subunit 5b: Devil Canyon, San
Diego County; land bounded by the
following UTM coordinates (E, N):
465000, 3702200; 464800, 3702200;
464800, 3702100; 464500, 3702100;
464500, 3702200; 464300, 3702200;
464300, 3702700; 464400, 3702700;
464400, 3702800; 464800, 3702800;
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464800, 3702700; 464900, 3702700;
464900, 3702600; 465000, 3702600;
returning to 465000, 3702200; and land
bounded by 465000, 3702200; 465166,
3702200; 465160, 3701865; 465246,
3701865; 465259, 3701960; 465500,
3701955; 465500, 3701500; 465400,
3701500; 465400, 3701300; 465300,
3701300; 465300, 3701200; 464800,
3701200; 464800, 3701300; 464700,
3701300; 464700, 3701700; 464800,
3701700; 464800, 3702000; 464900,
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3702000; 464900, 3702100; 465000,
3702100; returning to 465000, 3702200;
and land bounded by 465272, 3702200;
465400, 3702200; 465400, 3702100;
465500, 3702100; 465500, 3702078;
465261, 3702085; 465264, 3702184;
returning to 465272, 3702200.
(ii) Map of critical habitat Subunit 5b
for Brodiaea filifolia (Thread-leaved
brodiaea), follows:
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(7) Map Unit 8: San Marcos, San
Diego County, California, from USGS
1:24,000 quadrangle map San Marcos,
California.
(i) Subunit 8d: Upham; land bounded
by the following UTM coordinates (E,
N): 481588, 3666600; 481600, 3666600;
481600, 3666627; 481672, 3666791;
482059, 3666627; 481935, 3666339;
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481905, 3666339; 481800, 3666382;
481800, 3666400; 481758, 3666400;
481540, 3666490; returning to 481588,
3666600; and land bounded by: 481765,
3666200; 481800, 3666200; 481800,
3666266; 481893, 3666230; 481892,
3666214; 481890, 3666191; 481866,
3666173; 481848, 3666144; 481729,
3665850; 481700, 3665849; 481700,
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3665900; 481655, 3665990; 481635,
3666053; 481622, 3666069; 481612,
3666077; 481611, 3666077; 481600,
3666100; 481561, 3666100; 481401,
3666167; 481454, 3666290; 481750,
3666160; returning to 481765, 3666200.
(ii) Map of critical habitat Subunit 8d
for Brodiaea filifolia (Thread-leaved
brodiaea) follows:
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BILLING CODE 4310–55–C
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ER13DE05.004
Dated: November 30, 2005.
Craig Manson,
Assistant Secretary for Fish and Wildlife and
Parks.
[FR Doc. 05–23693 Filed 12–12–05; 8:45 am]
Agencies
[Federal Register Volume 70, Number 238 (Tuesday, December 13, 2005)]
[Rules and Regulations]
[Pages 73820-73863]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 05-23693]
[[Page 73819]]
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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 Brodiaea filifolia (thread-leaved brodiaea); Final Rule
Federal Register / Vol. 70, No. 238 / Tuesday, December 13, 2005 /
Rules and Regulations
[[Page 73820]]
-----------------------------------------------------------------------
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
RIN 1018-AT75
Endangered and Threatened Wildlife and Plants; Designation of
Critical Habitat for Brodiaea filifolia (thread-leaved brodiaea)
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: We, the Fish and Wildlife Service (Service), are designating
critical habitat for the federally threatened Brodiaea filifolia
(thread-leaved brodiaea) pursuant to the Endangered Species Act of
1973, as amended (Act). In total, approximately 597 acres (ac) (242
hectares (ha)) fall within the boundaries of the critical habitat
designation. The critical habitat is located in Los Angeles and San
Diego counties, California. Lands in Orange, Riverside, and San Diego
counties that are covered by approved and draft habitat conservation
plans are excluded under section 4(b)(2). Lands owned or controlled by
the Department of Defense that are covered by an Integrated Natural
Resource Management Plan (INRMP) that provides a benefit to the species
are exempt from critical habitat under section 4(a)(3) of the Act. As a
result of revisions based on peer and public comments and a re-
evaluation of methodology and mapping, approximately 4,093 ac (1,656
ha) in Los Angeles, San Bernardino, Orange, and San Diego counties
proposed as critical habitat were removed or excluded from this final
designation. Lands designated as critical habitat are under Federal and
private ownership. No Tribal lands are included in this critical
habitat designation.
DATES: This rule becomes effective on January 12, 2006.
ADDRESSES: Comments and materials received, as well as supporting
documentation used in the preparation of this final rule, are available
for public inspection, by appointment, during normal business hours, at
the Carlsbad Fish and Wildlife Office, 6010 Hidden Valley Road,
Carlsbad, CA 92011 (telephone 760-431-9440). The final rule, a list of
references cited, the economic analysis, and maps will also be
available on the Internet at https://carlsbad.fws.gov.
FOR FURTHER INFORMATION CONTACT: Field Supervisor, Carlsbad Fish and
Wildlife Office, at the above address (telephone 760-431-9440;
facsimile 760-431-9624).
SUPPLEMENTARY INFORMATION:
Designation of Critical Habitat Provides Little Additional Protection
to Species
In 30 years of implementing the Act, the Service has found that the
designation of statutory critical habitat provides little additional
protection to most listed species, while consuming significant amounts
of available conservation resources. The Service's present system for
designating critical habitat has evolved since its original statutory
prescription into a process that provides little real conservation
benefit, is driven by litigation and the courts rather than biology,
limits our ability to fully evaluate the science involved, consumes
enormous agency resources, and imposes huge social and economic costs.
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.
Role of Critical Habitat in Actual Practice of Administering and
Implementing the Act
While attention to and protection of habitat is paramount to
successful conservation actions, we have consistently found that, in
most circumstances, the designation of critical habitat is of little
additional value for most listed species, yet it consumes large amounts
of conservation resources. Sidle (1987) stated, ``Because the Act can
protect species with and without critical habitat designation, critical
habitat designation may be redundant to the other consultation
requirements of section 7.'' Currently, only 470 species or 37.5
percent of the 1,253 listed species in the U.S. under the jurisdiction
of the Service have designated critical habitat.
We address the habitat needs of all 1,253 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, and
the Section 10 incidental take permit process. The Service believes
that it is these measures that may make the difference for the
conservation of many species.
We note, however, that the August 6, 2004, Ninth Circuit judicial
opinion, Gifford Pinchot Task Force v. United States Fish and Wildlife
Service, found our definition of adverse modification was invalid. In
response to the decision, the Director has provided guidance to the
Service based on the statutory language. In this rule, our analysis of
the consequences and relative costs and benefits of the critical
habitat designation is based on application of the statute consistent
with the Ninth Circuit's ruling and the Director's guidance.
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
the limited listing funds are used to defend active lawsuits, to
respond to Notices of Intent (NOIs) 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 almost no ability to provide for adequate 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, is very
expensive, and in the final analysis provides relatively little
additional protection to listed 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). None of these costs result in
any benefit to the species that is not already afforded by the
protections of the Act enumerated
[[Page 73821]]
earlier, and they directly reduce the funds available for direct and
tangible conservation actions.
Background
By 1998, when the species was listed, at least 25 percent of the
known Brodiaea filifolia populations or occurrences had been eliminated
by urbanization and agricultural conversion (63 FR 54975, October 13,
1998). Urban development continues to be a threat to this species.
Habitat for the species is also threatened by off-road vehicle use;
non-agricultural grading and disking for weed control; clearing for
firebreaks; alteration of existing hydrologic conditions resulting from
construction and operation of flood control structures; over-grazing;
and competition from non-native plant species (USFWS 1998, RECON 1999,
CNDDB 2005). Occurrences of B. filifolia in Orange County and some in
San Diego County are threatened by the perennial Cynara cardunculus
(artichoke thistle or cardoon) (CNDDB 2005). B. filifolia and its
habitat are also threatened by dumping of manure and sewage sludge on
occupied habitat along the San Jacinto River in western Riverside
County (Roberts in litt. 2005). This material can alter the soil
chemistry and lead to changes in the vegetation sustainable on the
sites.
Previous Federal Actions
For more information on previous Federal actions concerning
Brodiaea filifolia, refer to the final rule listing the species as
threatened, published in the Federal Register on October 13, 1998 (63
FR 54975), and the proposed critical habitat designation published in
the Federal Register on December 8, 2004 (69 FR 71284). A recovery plan
for B. filifolia has not yet been completed. The following text
discusses Federal actions that occurred subsequent to the listing.
On November 15, 2001, a lawsuit was filed against the Department of
the Interior (DOI) and the Service by the Center for Biological
Diversity and California Native Plant Society, challenging our ``not
prudent'' determinations for eight plants, including Brodiaea filifolia
(Center for Biological Diversity et al. v. Department of the Interior
et al., CV 01-2101). A second lawsuit asserting the same challenge was
filed by the Building Industry Legal Defense Foundation (BILD) on
November 21, 2001 (Building Industry Legal Defense Foundation v.
Department of the Interior et al., CV 01-2145). Both cases were
consolidated on March 19, 2002, and all parties agreed to remand the
critical habitat determinations to the Service for additional
consideration. On July 1, 2002, the U.S. District Court for the
Southern District of California directed us to publish a new prudency
determination and, if prudent, propose critical habitat for B.
filifolia on or before November 30, 2004, and to publish a final rule
on or before November 30, 2005.
In the final listing rule, we determined that critical habitat was
not prudent for Brodiaea filifolia because such designation would
provide no benefit over that provided by listing on private property
where the species occurs (63 FR 54975). The courts have ruled that, in
the absence of a finding that the designation of critical habitat would
increase threats to a species, the existence of another type of
protection, even if it offers potentially greater protection to the
species, does not justify a ``'not prudent''' finding (Conservation
Council for Hawaii v. Babbitt 2 F. Supp. 2d 1280). Accordingly, we
withdrew our previous determination that the designation of critical
habitat was not prudent for B. filifolia and determined that critical
habitat designation for this species is prudent. We had sufficient
information necessary to identify specific features essential to the
conservation of B. filifolia and proposed critical habitat for this
species on December 8, 2004 (69 FR 71284). With the publication of this
rule, we are designating final critical habitat for B. filifolia in
compliance with the court's order.
Summary of Comments and Recommendations
We contacted appropriate Federal, State, and local agencies,
scientific organizations, and other interested parties and invited them
to comment on the proposed critical habitat designation. We also
invited public comment through the publication of notices on December
17, 2004, in The Press-Enterprise, Riverside, CA; San Diego Union-
Tribune, San Diego, CA; Orange County Register, Santa Ana, CA; and the
Los Angeles Times, Los Angeles, CA. The initial comment period ended
February 7, 2005. There were no requests for public hearings.
During the comment period that opened on December 8, 2004, and
closed on February 7, 2005, we received 19 comment letters directly
addressing the proposed critical habitat designation: 4 comment letters
were received from 3 peer reviewers, 2 from Federal agencies, and 13
from organizations or individuals. We received 2 additional comment
letters that were illegible. We attempted to contact the authors of the
letters but received no response; therefore, we could not consider the
information. Thirteen commenters supported the designation of critical
habitat for Brodiaea filifolia, and three opposed the designation.
Three letters included comments or information, but did not express
support or opposition to the proposed designation.
A second comment period to consider the draft economic analysis of
proposed critical habitat for Brodiaea filifolia opened on October 6,
2005, and closed on October 20, 2005. During the comment period we
received 6 letters: 5 from organizations or individuals and 1 from a
local government agency. In opening the comment period on the draft
economic analysis, we also reopened the comment period on our critical
habitat proposal. Comments received during both comment periods were
grouped into general issue categories relating to the proposed
designation or the draft economic analysis.
Peer Review
In accordance with our joint policy published on July 1, 1994 (59
FR 34270), we solicited review of our proposed rule from at least three
appropriate independent specialists/experts. The purpose of such review
is to ensure our final designation is based on scientifically sound
data, assumptions, and analyses. We solicited peer review from four
knowledgeable individuals with scientific expertise that included
familiarity with the species, the geographic region in which the
species occurs, and conservation biology principles. We received
responses from three of the peer reviewers. The peer reviewers
supported the designation; however, they expressed concern about errors
and omissions in the proposal, including the exclusion of critical
habitat on lands covered by Habitat Conservation Plans (HCP). Comments
from peer reviewers and other commenters are addressed in the following
summary, and corrections and information are incorporated into the
final rule as appropriate.
Peer Reviewer Comments Related to Previous Federal Actions, the Act,
and Implementing Regulations
Similar comments that were received from other commenters are
addressed in this section to avoid redundancy.
(1) Comment: Two peer reviewers requested that we provide a review
of the unique status of plants under the Act, including the limited
protection plants are provided under section 9 of the Act and the pros
and cons of critical habitat designation for plants. Another
[[Page 73822]]
commenter indicated that Brodiaea filifolia receives substantial
protection under the California Endangered Species Act (CESA) and the
California Environmental Quality Act (CEQA) and does not require
special management considerations or protection.
Our Response: Brodiaea filifolia is listed as an endangered species
under the CESA. This allows the species to receive greater attention
during the land use planning process by local governments, public
agencies, and landowners. State listed plants are protected from
removal, except by permit or agreement from the California Department
of Fish and Game (CDFG). However, listing under the CESA doesn't remove
all conservation threats to the species. Areas that contain features
essential to the conservation of B. filifolia and that may require
special management considerations or protection would still warrant
critical habitat designation under the Act. The benefits and
limitations of critical habitat designation for B. filifolia are
addressed in several different sections throughout this document,
including the ``Effects of Critical Habitat Designation,'' and
``Application of Section 3(5)(A), Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the Act.''
Peer Reviewer Comments Related to Life History, Habitat
Characteristics, and Ecological Considerations
(2) Comment: Three peer reviewers and five other commenters
provided additional information, clarifications, and references for
aspects of the biology, associated vegetation, and soil preferences of
Brodiaea filifolia. One peer reviewer considered ours an excellent
overview of the biology of the species but lacking two references they
cited.
Our Response: We appreciate additional information and
clarification and, where appropriate, we have incorporated this into
the final rule.
(3) Comment: One peer reviewer and one individual stated that we
should have cited more recent information, including the California
Natural Diversity Database (CNDDB), regarding the historical range of
Brodiaea filifolia, pointing out that some new occurrences have been
discovered.
Our Response: In developing the proposed rule we used data compiled
from the CNDDB database in 2003 as well as an update in 2004 (CNDDB
2003; 2004). This is a running database that includes periodic updates
of existing occurrence information and new occurrence records. There
was one occurrence of Brodiaea filifolia identified in the 2004 update
of the CNDDB that we overlooked. This occurrence is located in an
unincorporated area of central San Diego County near Lake Hodges.
Fortunately, this occurrence of about 688 plants is being conserved
under a Minor Amendment to the San Diego County MSCP.
Another occurrence in the same area was not entered into the CNDDB
until April 6, 2005 (CNDDB 2005); therefore, we were not able to
consider it in the proposed rule. It is not possible to include an area
in this final critical habitat designation that was not identified in
the proposed rule. Because we are under a court deadline to complete
this final rule, the publication of a revised proposed rule to include
this area for public review and comment could not have been completed
in time to comply with the court's deadline.
(4) Comment: One peer reviewer cites the dumping of sewage sludge
as the most serious threat to Brodiaea filifolia along the San Jacinto
River habitat in Riverside County. The peer reviewer also stated that
these deposits alter the soil chemistry.
Our Response: This comment is appreciated and a discussion of this
threat has been incorporated into the ``Background'' section of this
final rule.
(5) Comment: A peer reviewer and two individuals provided differing
views on the issue of translocation. One view asserted that
translocation may not have a high chance for success. The other
perspective considers it premature to state that translocation is a
threat to the species. One peer reviewer requested that we discuss all
of the translocated populations.
Our Response: We are uncertain about the long-term viability of
translocated populations and their contribution to the species as a
whole, therefore, we did not specifically include them in this
designation. However, translocated populations may contribute to the
long-term survival and recovery of the species. Additional long-term
monitoring for genetic diversity and the reproductive impact of these
populations is warranted. Only issues specifically related to the
critical habitat designation are discussed in this final rule,
therefore, we have not included a broad overview of translocated
populations in this document.
Peer Reviewer Comments Related to Critical Habitat, Primary Constituent
Elements, and Methodology
(6) Comment: Two peer reviewers and two other commenters expressed
concern about errors and lack of attribution to citations in the
proposed rule, suggesting that it be rewritten and re-released. Several
questions, additions, and corrections to statements and information
relating to proposed critical habitat units were provided by peer
reviewers and other commenters.
Our Response: Because of a court deadline to complete this final
rule, we could not publish a revised proposed rule for public review
and comment in time to comply with the court's deadline. One of the
purposes of releasing the proposed rule and draft economic analysis for
public review and comment is to obtain substantive information and
materials related to the proposed critical habitat designation. We
appreciate receiving additional information, corrections, and
clarifications that were useful in our re-evaluation of the proposed
units and unit descriptions. Where appropriate, we have included this
information and answers to specific questions in the final rule. See
the ``Summary of Changes from Proposed Rule'' section for a review of
changes in the final designation.
(7) Comment: One peer reviewer stated that we did not provide
information on our reasoning for proposing critical habitat in a number
of locations in Riverside and San Diego counties.
Our Response: We have re-evaluated areas included in proposed
critical habitat. This final designation reflects mapping refinements,
our re-evaluation of proposed areas under section 3(5)(A), and
exclusions under sections 4(a)(3) and 4(b)(2) of the Act. Please refer
to the ``Criteria Used to Identify Critical Habitat,'' and the
``Application of Section 3(5)(A), Exemption Under Section 4(a)(3) and
Exclusions Under Section 4(b)(2) of the Act'' for more information.
(8) Comment: Two peer reviewers suggested literature citations,
with one requesting that we cite final versions rather than draft
documents, and the other requesting that the references cited list be
published with the text of the rule and posted on the Internet.
Our Response: Where appropriate, we have incorporated these
suggestions in this rule. We cite the most current version of documents
available. As stated in the ``References Cited'' section of the rule, a
list of references cited is available upon request from the Carlsbad
Fish and Wildlife Office. We will also make this list available on the
Internet at https://carlsbad.fws.gov.
(9) Comment: One peer reviewer and a public commenter questioned
our use of a draft version of Bramlet and White 2004 (erroneously cited
as White and Bramlet 2004 in the proposed rule).
[[Page 73823]]
Our Response: We referred to a working table of occurrences (Table
3) during the preparation of the proposed rule. The information in this
table was considered to be one of the best available on the occurrences
of Brodiaea filifolia. Only occurrences corroborated from other sources
are considered in this final rule.
(10) Comment: Two peer reviewers and two public commenters
variously stated that the section of the proposed rule titled
``Designation of Critical Habitat Provides Little Additional Benefit to
Species'' is generic, editorializing, out of place in a proposal, and
political. One commenter wanted us to point to the research that
specifically justifies this claim in relation to Brodiaea filifolia.
Our Response: The section referenced by the commenters is intended
to be a general statement regarding our position on the designation of
critical habitat. As discussed in the preamble of this and other
critical habitat designation rules, we believe that, in most cases,
conservation mechanisms provided through section 7, 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 programs with private
and public landowners and Tribes provide greater incentives and
conservation benefits than does the designation of critical habitat.
(11) Comment: One peer reviewer and one commenter requested a
definition of PCE. They also suggested clarifications for PCEs relating
to habitat descriptions, soil types, slopes, and associated vegetation
types.
Our Response: As stated in the ``Primary Constituent Elements''
(PCE) section of the proposed rule (69 FR 71284), PCEs are those
physical or biological features essential to the conservation of a
species, and that may require special management considerations or
protection. The PCEs for Brodiaea filifolia were based on the best
available information relating to the species' occurrences and its soil
and vegetation associations. Please refer to the ``Methods'' section of
this final rule for a discussion of all information sources used to
define the PCEs for B. filifolia.
(12) Comment: Two peer reviewers noted the ability of Brodiaea
filifolia to persist on disturbed, degraded, or disked sites and the
suitability of these sites if allowed to recover, especially by natural
flooding processes.
Our Response: It is likely that some areas supporting occurrences
of Brodiaea filifolia have been degraded to some degree. The areas
included in proposed critical habitat and areas excluded from proposed
designation under section 4(b)(2) of the Act were identified as being
occupied and containing the physical or biological features essential
to the conservation of the species. Lands included in this final
designation are occupied and contain the features essential to the
conservation of B. filifolia. Please refer to the ``Application of
Section 3(5)(A), Exemption Under 4(a)(3), and Exclusions Under Section
4(b)(2) of the Act'' section for information about areas removed,
exempted, or excluded from critical habitat.
(13) Comment: Two peer reviewers and three other commenters
provided information and suggestions related to the species' biology,
habitat description, and condition, as well as boundaries of the
critical habitat subunits and areas containing habitat with features
essential to the conservation of this species that were excluded from
critical habitat in our proposal. One peer reviewer also noted that
some units included unsuitable habitat. One commenter recommended we
change the configuration of boundaries in the Rancho Santalina/Loma
Alta subunit to better represent the areas containing features
essential to the conservation of Brodiaea filifolia.
Our Response: We appreciate the information and suggestions from
these commenters and, where appropriate, we have incorporated the
information on subunit descriptions into this final rule. Some of the
commenters discussed making the boundaries of critical habitat subunits
and areas containing habitat with features essential to the
conservation of this species more precise. We made such changes where
appropriate. We have attempted to map the boundaries to exclude
developed land; however, we may not have been able to exclude all
developed land or land that does not contain the PCEs. Any such
structures and the land under them inadvertently left inside the mapped
critical habitat boundaries have been excluded in the text portion of
the rule, and are not designated as critical habitat. Federal actions
limited to these areas would not trigger section 7 consultations,
unless they affect the species and/or primary constituent elements in
adjacent critical habitat.
Some commenters suggested including additional areas in the
proposed subunits or making boundary adjustments in areas containing
features essential to the conservation of the species that were
excluded from proposed designation. However, these commenters did not
provide sufficient site-specific data for us to adequately evaluate
their recommendations. We reviewed the proposed Santalina/Loma Alta
subunit and determined it does not meet the definition of critical
habitat under section 3(5)(A) of the Act. Please refer to the section
``Application of Section 3(5)(A), Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the Act'' for more information.
(14) Comment: Two peer reviewers and one commenter questioned our
use of occurrences with 1,000 or more plants as a measure of whether an
area contained habitat with features essential to the conservation of
Brodiaea filifolia. One commenter questioned the science behind our
decision not to propose all occurrences of B. filifolia in Orange and
San Diego counties as critical habitat.
Our Response: In developing our proposal, we relied on several
types of information to determine whether an occurrence of Brodiaea
filifolia was considered significant. As outlined in the ``Criteria
Used to Identify Critical Habitat'' section, we evaluated population
estimates, soil types, associated vegetation, and elevation. We also
evaluated the location of occurrences in relation to the range of the
species. For example, occurrences that supported less than 1,000
plants, but which were on alkali playas were considered to be
significant. For an explanation of why more areas in Orange and San
Diego counties were not included in the final designation, please refer
to the ``Application of Section 3(5)(A), Exemption Under Section
4(a)(3) and Exclusions Under Section 4(b)(2) of the Act'' portion of
this rule.
(15) Comment: One peer reviewer and one individual questioned the
value of including small units (e.g., 6b (Mesa Drive)), or those with
few plants (e.g., subunits 4d (Prima Deschecha), 4f (Talega/Segunda
Deschecha), and 6a (Alta Creek)) as critical habitat.
Our Response: We considered occurrence information, soil types,
vegetation association and other factors in our re-evaluation of
proposed subunits. As a result of our re-evaluation, several proposed
subunits, including 4d, 4f, and 6a, were removed from final
designation. Subunit 6b (Mesa Drive) is relatively small, covering
about 5 ac (2 ha), but it supports a significant occurrence of Brodiaea
filifolia and contains features essential to the conservation of the
species; therefore, it was included in proposed critical habitat.
However, subunit 6b was excluded from final designation under section
4(b)(2) of the Act. Please see the ``Summary of Changes from Proposed
Rule,'' and
[[Page 73824]]
``Application of Section 3(5)(A), Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the Act'' sections for more
information.
(16) Comment: One peer reviewer recommended that we add Domino or
Chino alkali soils to the description of PCEs because Brodiaea
filifolia occurs on these soil types in Riverside County.
Our Response: We have reviewed this information and have included
these soil types in our definition of the PCEs for Brodiaea filifolia.
(17) Comment: Two peer reviewers and one Federal agency commenter
questioned our inclusion of subunits 5a (Miller Mountain) and 5b (Devil
Canyon) in proposed critical habitat because most plants in subunit 5a
and some in subunit 5b are hybrids between Brodiaea filifolia and
Brodiaea orcuttii. One peer reviewer noted that hybrids occur in the
City of San Marcos and on Marine Corps Base, Camp Pendleton (Camp
Pendleton), although specific numbers and locations were not provided.
One peer reviewer stated that plants in areas containing features
essential to the conservation of the species in Riverside County are
prone to hybridization. Another commenter, knowledgeable about the
genetics of Brodiaea, stated that B. filifolia and B. orcuttii form a
unique line and could hybridize only with each other.
Our Response: We acknowledge that within subunits 5a and 5b, there
are substantial numbers of plants that are hybrids of Brodiaea
filifolia and Brodiaea orcuttii (Boyd et al. 1992). The population in
subunit 5a is considered to be largely hybridized and we cannot
determine that they can be considered as contributors to the long-term
conservation of the species; therefore, we removed this subunit from
consideration. Although plants in subunit 5b also show some
hybridization, the extent of the hybridization is less. The occurrence
of B. filifolia in subunit 5b is significant and is found at one of the
highest elevations within the range of the species. We have included
the portion of land in subunit 5b that is occupied by B. filifolia and
contains features essential to the conservation of the species in this
final designation. Please see the ``Summary of Changes from Proposed
Rule'' and ``Application of Section 3(5)(A), Exemption Under Section
4(a)(3), and Exclusions Under Section 4(b)(2) of the Act,'' and ``Unit
Descriptions'' sections for more information.
We are aware of a CNDDB (Element Occurrence 10) report in the City
of San Marcos that included a reference to the possible presence of
hybrids between Brodiaea filifolia and B. jolonensis. This area was
identified as subunit 8d (Upham) in our proposed rule. It has been
reported that putative hybrid individuals of B. filifolia and another
species that has been erroneously referred to B. jolonensis occur on
the site (Armstrong 2005). Though these hybrid plants exhibit
intermediate characteristics between the two theorized parental
species, a third species, B. orcuttii, also grows nearby within the
unit. According to Armstrong (2005), the hybrid plants appeared to be a
``clonal population'' restricted to ``a one acre area at the southwest
end of the property'' and that these individuals ``probably reproduced
asexually through cormlets.'' Although Armstrong (2005) found
``numerous B. filifolia, B. orcuttii, and (the material referred to as
B. jolonensis)'' growing within the unit in May 2005, he failed to
observe any of the hybrid plants. As a result, although putative
hybridization has been reported for this unit, hybrid plants are either
no longer present or they represent an undetectable, small fraction of
the overall population of B. filifolia. The occurrence of B. filifolia
in this subunit is estimated to support about 1,000 plants and contains
features essential to the conservation of the species.
We were not able to confirm the commenter's reference to hybrids on
Camp Pendleton.
(18) Comment: One peer reviewer considered the mapping of lands in
Riverside County that were excluded from proposed critical habitat to
be inadequate. One individual requested UTMs for these same areas.
Our Response: As stated in the proposed rule, maps of the areas in
Riverside County containing features essential to the conservation of
Brodiaea filifolia that were excluded under section 4(b)(2) of the Act,
based on conservation measures outlined in the Western Riverside County
Multiple Species Habitat Conservation Plan (MSHCP), were available on
our Web site. We believe that the general public finds these maps more
useful than the UTM coordinates. Also, GIS layers of the areas proposed
for critical habitat designation as well as areas excluded from
proposed critical habitat are available upon request from our office.
We will clarify the availability of this information in future critical
habitat rules.
(19) Comment: One peer reviewer expressed the importance of
designating critical habitat for Brodiaea filifolia in irregularly
flooded bottomland areas of the San Jacinto River floodplain because of
concerns that alteration of the floodplain could adversely modify a
significant portion of the Riverside County occurrences of the plant
and eliminate a unique element of the species' habitat associations
(i.e., plants adapted to alkali soils). The reviewer stated that
designation of critical habitat in the San Jacinto River floodplain
area would strengthen the regulatory effectiveness of section 7 by
adding ``adverse modification'' to the jeopardy standard available to
the Service and ensure that activities of the U.S. Army Corps of
Engineers (ACOE) do not adversely modify the habitat. The reviewer also
indicated that thousands of acres are undergoing alteration by sewage
sludge and manure dumping.
Our Response: We agree that areas supporting Brodiaea filifolia in
the San Jacinto River floodplain are important because they contain
features essential to the conservation of the species. However, these
areas have been excluded from critical habitat because the Western
Riverside County MSHCP addresses the conservation needs of the species,
including the maintenance of floodplain processes along the San Jacinto
River. The Secretary has determined the benefits of excluding lands
covered by the Western Riverside County MSHCP outweigh the benefits of
including them in critical habitat (see the ``Application of Section
3(5)(A), Exemption Under Section 4(a)(3), and Exclusions Under Section
4(b)(2) of the Act'' section of this rule.)
(20) Comment: Two peer reviewers and one individual commenter
stated that areas we identified as having features essential to the
conservation of Brodiaea filifolia near the City of Corona and in
Moreno Valley in Riverside County are erroneous and based on an early
draft of the Western Riverside County MSHCP. The commenter suggested
they might be derived from questionable biological surveys.
Our Response: We appreciate the correction. After further
evaluation, we did not find reliable data validating the occurrences of
Brodiaea filifolia at these locations, and we removed them from
consideration. For more information, please refer to the ``Summary of
Changes from Proposed Rule.''
(21) Comment: One peer reviewer suggested that we designate habitat
blocks that contain the entire San Jacinto River floodplain to capture
the historical habitat of the species.
Our Response: When designating critical habitat for Brodiaea
filifolia we identified land containing physical or biological features
essential to the conservation of the species and which may require
special management considerations or protection. Physical or
[[Page 73825]]
biological features include areas needed for pollen dispersal and
pollination; seed dispersal and germination, and maintenance of seed
banks; and areas that provide the basic requirements for growth. These
features, referred to as PCEs, are discussed in the ``Primary
Constituent Elements'' section of this rule. Areas in western Riverside
County, including lands within the San Jacinto River floodplain that
are occupied by B. filifolia and contain features essential to the
conservation of the species have been excluded from critical habitat
pursuant to section 4(b)(2) of the Act (see ``Application of Section
3(5)(A), Exemption Under Section 4(a)(3), and Exclusions Under Section
4(b)(2) of the Act.'')
(22) Comment: One peer reviewer questioned how land management of
reserves helps recovery of the species with and without critical
habitat.
Our Response: We are assuming the peer reviewer is referring
specifically to reserves that are established in conjunction with HCPs.
Approved HCPs include measures to monitor, minimize, and mitigate
impacts; and must provide adequate funding. Management of reserves in
accordance with an HCP's issuance criteria would be carried our
regardless of a critical habitat designation on identified reserve
lands. Only actions authorized, funded, or carried out by a Federal
agency that may affect critical habitat would require consultation with
us and would not affect actions undertaken on reserve areas that do not
have a Federal nexus. Reserves established as part of an HCP include
monitoring and management to ensure the areas retain their biological
value for the species.
Peer Review Comments Related to Department of Defense (DoD) Lands
(23) Comment: One peer reviewer requested a discussion of the
importance of populations of Brodiaea filifolia on Camp Pendleton.
Our Response: Populations of Brodiaea filifolia on Camp Pendleton
are of considerable importance not only because of the numbers of
plants reported (over 4,000) from several different occurrences, but
also because they are found in more than one vegetation or soil
association, including grasslands and vernal pools; the occurrences are
distributed in a manner that likely facilitates pollen transfer among
them and also with occurrences to the north and south of Camp
Pendleton. Please see the ``Application of Section 3(5)(A), Exemption
Under Section 4(a)(3), and Exclusions Under Section 4(b)(2) of the
Act'' for more information about Camp Pendleton's Integrated Natural
Resource Management Plan (INRMP) and other measures Camp Pendleton is
undertaking to address B. filifolia on their lands.
Peer Review Comments Related to the NCCP/HCP Program, Section 7, and
Section 404
(24) Comment: Two peer reviewers and one commenter disagreed with
our determination to exclude critical habitat based on approved HCPs.
One peer reviewer expressed further concern that it is uncertain
whether HCPs will protect these areas because no specific preserve
boundaries have been proposed, relying instead on goals and potential
conservation. The reviewers stated that we did not provide a clear
biological reason for excluding lands covered by HCPs and questioned
why more areas were not determined to be critical habitat.
Our Response: Under section 4(b)(2) of the Act, the Secretary may
exclude any particular area from critical habitat designation if the
benefits of excluding such area outweigh the benefits of including it
in critical habitat, unless it is determined, based on the best
scientific and commercial data available, that the failure to designate
such area as critical habitat will result in the extinction of the
species. We evaluated the benefits of excluding critical habitat on
lands covered by HCPs, including the Western Riverside County MSHCP,
the San Diego County Multiple Habitat Conservation Plan (MHCP) and its
approved subarea plans, the Orange County Central and Coastal NCCP/HCP,
and the Settlement Agreement for Rancho Mission Viejo's Ranch Plan, a
component of the draft Orange County Southern Subregion NCCP/HCP,
against the benefits of including such lands in critical habitat. A
major benefit of excluding these lands from critical habitat is the
facilitation of continued partnerships with the various signatory
agencies, cities and landowners involved with these NCCP/HCP efforts.
Although a possible benefit of including these lands in critical
habitat would be to enhance education about the species and its habitat
needs, we consider this benefit to have largely been met through the
public participation process that occurred, and continues to occur,
during the development and implementation of these conservation
planning efforts. We acknowledge that the Western Riverside County
MSHCP does not describe a hard-lined reserve, but it does identify
specific conservation goals and objectives for Brodiaea filifolia,
including the conservation of 11 occurrences in the two Core Areas in
western Riverside County where this species is found.
Please refer to the ``Application of Section 3(5)(A), Exemption
Under Section 4(a)(3), and Exclusions Under Section 4(b)(2) of the
Act'' section for more discussion of the Western Riverside County MSHCP
and other NCCP/HCP efforts.
(25) Comment: Two peer reviewers state that the Lakeview/Nuevo Area
Plan (Dudek and Associates 2003) is inconsistent with provisions of the
Western Riverside County MSHCP because it has nearly the entire
Criteria Area zoned for residential development.
Our Response: Under the Western Riverside County MSHCP, permittees
are obligated to adopt and maintain ordinances or resolutions as
necessary, and amend their general plans as appropriate, to implement
the requirements and fulfill the purposes of the MSHCP and its
associated Implementing Agreement (IA) and Permit (Dudek and Associates
2003).
(26) Comment: Two peer reviewers requested that we discuss specific
conservation actions under the Western Riverside County MSHCP that will
result in conservation of Brodiaea filifolia. One reviewer specifically
asked what assurances are in place that conservation benefits will
occur before Highway 79 is built through habitat for the species.
Our Response: The Western Riverside County MSHCP identifies
specific goals to be implemented for long-term conservation of Brodiaea
filifolia, including conservation of at least 6,900 ac (2,760 ha) of
habitat, containing 11 major locations supporting the species,
conducting surveys for B. filifolia in certain areas, and maintaining
floodplain processes along the San Jacinto River.
The assembly of the MSHCP Conservation Area is anticipated to occur
over a period of time during the life of the Permit. To ensure that the
resources ultimately conveyed to the MSHCP Conservation Area are
maintained in their existing condition prior to reserve assembly, the
MSHCP permittees are obligated to adopt and maintain ordinances or
resolutions and to amend their general plans such that they will be
able to meet their obligations under the MSHCP (Dudek and Associates,
Inc. 2003; 2003b).
Several covered activities discussed under the MSHCP have the
potential to impact populations of Brodiaea filifolia within the
proposed MSHCP Conservation Area, including the San Jacinto River Flood
Control Project and the State Route 79 Realignment Project.
[[Page 73826]]
These projects will require additional consultation with our agency
under section 7 of the Act (Dudek and Associates, Inc. 2003).
As a result of informal consultation conducted to date on the State
Route 79 Realignment Project, the City of Hemet has adopted an Interim
Urgency Ordinance that preserves two avoidance alternatives for the
State Route 79 Realignment Project, both of which are located outside
of the MSHCP Criteria Area, and also allows the City to ensure that
development efforts within the MSHCP Criteria Area are coordinated such
that habitat conserved within the Criteria Area does not become
fragmented, thereby allowing the City to meet their obligations under
the MSHCP (City of Hemet 2005).
(27) Comment: One peer reviewer stated that there was no protection
of land for Brodiaea filifolia before the approval of the Western
Riverside County MSHCP, and there is no protection now, as evidenced by
the ongoing dumping of sewage sludge and manure on occupied habitat.
The reviewer cited an area along Case Road where dumping has occurred.
Our Response: Permittees under the Western Riverside County MSHCP
are obligated to adopt and maintain ordinances or resolutions as
necessary, and amend their general plans as appropriate, to implement
the requirements and to fulfill the purposes of the MSHCP and its
associated IA and Permit (Dudek and Associates, Inc. 2003; 2003b). The
Western Riverside County MSHCP is a large, complex habitat conservation
plan, and its implementation is expected to take time. In its first
year of implementation, the Western Riverside County MSHCP has already
resulted in conservation and management actions that address threats to
Brodiaea filifolia on private lands. For example, the City of Hemet has
adopted an ordinance that has halted the dumping of manure within the
City (City of Hemet 2002).
(28) Comment: One peer reviewer expressed concern that there is no
assurance that prioritization of conservation areas following the
criteria of the Western Riverside County MSHCP will select the more
favorable biological areas over less favorable areas. For example,
while the Western Riverside County MSHCP proposes one method of
conservation, another, yet to be disclosed method, could prevail.
Our Response: We refer the reader to our responses to comments 24
and 26 above and to the section titled ``Application of Section
3(5)(A), Exemption Under Section 4(a)(3), and Exclusions Under Section
4(b)(2) of the Act'' for more information.
(29) Comment: One peer reviewer, citing the Fieldstone/La Costa
Associates HCP/Ongoing Multi-species Plan (known as the Villages of La
Costa HCP), approved about 10 years ago, states that HCPs are supposed
to provide for monitoring of the status of covered species to measure
the success of conservation measures and asked us to document the
status of the reserve.
Our Response: Conservation provisions for Brodiaea filifolia
outlined in the Villages of La Costa HCP include protection of almost
6,000 plants in an open-space preserve with long-term management and
monitoring, habitat restoration, and control of invasive plant species.
Further information about this HCP can be found in the section titled
``Application of Section 3(5)(A), Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the Act.''
Public Comments Related to Life History, Habitat Characteristics, and
Ecological Considerations
(30) Comment: One commenter criticized our use of foraging distance
data based on Bombus taxa (bumblebees), stating that their studies had
not recorded a single instance of bumblebees visiting Brodiaea
filifolia on their property.
Our Response: We believe our use of the 820 feet (ft) (250 meters
(m)) distance for pollinator movement and habitat is justified. Bell
and Rey (1991) noted Bombus californicus as one of the native bees
observed pollinating Brodiaea filifolia on the Santa Rosa Plateau in
Riverside County. Please see the ``Criteria Used to Identify Critical
Habitat'' section for a detailed discussion.
(31) Comment: One commenter criticized our omission of a study of
pollinators conducted by Rancho Mission Viejo.
Our Response: The omission of this report was inadvertent. The
report summarizes field studies conducted in late spring 2003 and
reports insects visiting flowers of Brodiaea filifolia at two locations
and two times during the season. Observations were made on three dates
between April and May 2003. Burrowing bees (Anthophoridae), Sweat bees
(Halictidae), and Flower-loving flies (Syrphidae) were the most common
groups of insects observed, although it is not clear from the report
whether pollination by the various insects was confirmed by
observations of fruit production by the plants. Information from this
report is incorporated, where appropriate, in this final rule.
Public Comments Related to Critical Habitat, Primary Constituent
Elements, and Methodology
(32) Comment: One commenter suggested a method for designing the
size of conservation areas based on Burgman et al. (2001).
Our Response: Although the information is appreciated, it is
important to clarify the differences between establishment of
conservation areas and the designation of critical habitat. The
designation of critical habitat does not establish reserves, preserves,
wilderness areas, refuges or other types of conservation areas. We
suggest readers refer to the sections on ``Methods,'' ``Primary
Constituent Elements,'' and ``Effects of Critical Habitat Designation''
to more fully understand how we identified areas for critical habitat
designation, the features essential to the conservation of the species,
and the effect of critical habitat on landowners.
(33) Comment: One commenter wanted to know how many occurrences in
Riverside and San Diego counties are outside designated critical
habitat and how this would affect the viability of the species.
Our Response: A number of occurrences in Riverside and San Diego
counties were not proposed for designation because they were not
considered significant occurrences, or were excluded from proposed
critical habitat under section 4(b)(2) of the Act. Many of these areas
receive conservation consideration under existing INRMPs, HCPs, or
other conservation instruments. Please refer to the ``Application of
Section 3(5)(A), Exemption Under Section 4(a)(3), and Exclusions Under
Section 4(b)(2) of the Act'' for more information. Please note that,
although habitat for Brodiaea filifolia may be outside the boundaries
of designated critical habitat, it does not mean these areas are
unimportant or may not be necessary for recovery of the species.
(34) Comment: One commenter stated that the purpose of critical
habitat under section 3 of the Act is to facilitate recovery of species
and that it should include the opportunity for genetic exchange,
migration, and changes in climate.
Our Response: The definition of critical habitat has two prongs,
that is, one prong considers specific areas within the geographic area
occupied by the species and the second prong considers specific areas
outside the geographic area occupied by the species.
[[Page 73827]]
To the extent that we can relate genetic exchange, migration, and
changes in climate to physical and biological features essential to the
conservation of the species and those areas also require special
management considerations or protection (prong one) or based upon a
determination by the Secretary that an unoccupied area is essential to
the conservation of the species (prong two), we may and do consider
those factors in our designation of critical habitat. Please see the
``Designation of Critical Habitat Provides Little Additional Protection
to Species'' section and the ``Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and Exclusions Under Section 4(b)(2)
of the Act'' for more information and discussion.
(35) Comment: One commenter stated there is a poor record of
recovery for species with critical habitat while another commenter
cited a report indicating that species with critical habitat are less
likely to be in decline and twice as likely to be recovering.
Our Response: The Service has been unable to independently verify
the results of such studies. The fact that there are conflicting
studies shows that the issue has not been settled. The Service believes
that most of the protections of the Act come with listing the species,
and by far the most successful recovery efforts come from voluntary
partnerships. Critical habitat designation is not the sole means by
which conservation of a species may be addressed.
(36) Comment: One commenter characterized our proposed rule as a
sweeping designation that exceeds our congressional mandate. The
commenter further stated that our designation should be based on the
estimated 825 ac (334 ha) of land occupied by Brodiaea filifolia
identified in the final listing rule (63 FR 54975). Another commenter
stated that Congress intended for critical habitat to be extremely
narrowly defined and limited only to areas necessary to bring the
species to a point where it is no longer in danger of extinction.
Our Response: In developing the final critical habitat designation
for B. filifolia, we reviewed all information and data received during
the two public comment periods and have removed from consideration
those lands that do not meet the criteria for designation. Specific
areas included in this final designation contain the physical or
biological features essential to the conservation of B. filifolia,
including space for pollen dispersal and pollination; seed dispersal
and germination, and maintenance of seed banks; and areas that provide
the basic requirements for growth. Please refer to the ``Summary of
Changes From Proposed Rule,'' and ``Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and Exclusions Under Section 4(b)(2)
of the Act'' sections of this rule for more information.
(37) Comment: One commenter requested that we indicate which
parcels within critical habitat units/subunits contain the PCEs. The
commenter also stated that all lands within proposed units/subunits may
not contain all of the PCEs.
Our Response: In re-evaluating areas proposed as critical habitat
for Brodiaea filifolia, we determined that some areas do not contain
features essential to the conservation of the plant, and therefore were
removed from final designation. The ``Summary of Changes from Proposed
Rule'' and ``Application of Section 3(5)(A), Exemption Under Section
4(a)(3), and Exclusions Under Section 4(b)(2) of the Act'' sections
provide information about areas removed from final designation. Due to
the scale at which we map critical habitat boundaries, we do not
include parcel level detail. If lands within the boundaries of critical
habitat units/subunits do not contain any PCEs, then they have been
excluded from the designation in the text portion of the rule.
(38) Comment: One commenter stated that it was not good science to
``extrapolate'' genetic information from studies on a ``ubiquitous
genera'' such as Lasthenia (lasthenia) to narrow endemic species such
as Brodiaea filifolia.
Our Response: We cited the reference to Lasthenia to highlight the
significance of outlying portions of a species' range to its genetic
diversity. Ornduff (1966) cites several species of Lasthenia with
morphological or cytological variants at the margins of their
distributions. One example used was Lasthenia fremontii, restricted to
vernal pools or wet meadows in the Central Valley. This example was
cited for the purposes of explaining how peripheral populations of
Brodiaea filifolia may be important to maintaining the genetic
diversity of the taxa.
(39) Comment: Two commenters questioned our 820 ft (250 m)
pollinator movement and habitat area. One commenter thought it was too
narrow, the other thought it was too wide. One cited a reference that
one group of bees (halictids) forage no more than 328 ft (100 m).
Our Response: We have included additional references and discussion
in the ``Background'' section of this rule to support our use of 820 ft
(250 m) for a pollinator movement and habitat area. Please see the
``Background'' and ``Criteria Used to Identify Critical Habitat''
sections for a detailed discussion.
Public Comments Related to Department of Defense Lands
(40) Comment: One Federal agency commenter agreed with our
exclusion of mission-critical areas on Camp Pendleton from critical
habitat designation under section 4(b)(2) of the Act; however, they
strongly disagreed with our determination in the proposed rule that
Camp Pendleton's Integrated Natural Resource Management Plan (INRMP)
does not provide a benefit for Brodiaea filifolia. The commenter
characterized critical habitat as encroachment that would unacceptably
degrade Camp Pendleton's mission. The commenter also provided
information about programs and activities carried out under the INRMP
for B. filifolia.
Our Response: We appreciate the information from the commenter and
have reviewed Camp Pendleton's INRMP, completed in November 2001 (U.S.
Marine Corps 2001). Based on our review of the INRMP and information
provided by the commenter, we determined that the INRMP provides a
benefit for Brodiaea filifolia and have exempted Camp Pendleton from
critical habitat designation pursuant to section 4(a)(3) of the Act. We
have also determined that exclusion of Camp Pendleton pursuant to
section 4(b)(2) of the Act is also appropriate. Please see the
``Application of Section 3(5)(A), Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the Act'' section for more
information.
(41) Comment: One commenter claimed we are inconsistent in
excluding Camp Pendleton from critical habitat designation while other
military installations have critical habitat on their lands.
Our Response: The commenter did not cite which military
installation(s) had critical habitat designation(s); therefore, we
cannot provide specific information about a particular installation.
Under section 4(b)(2) of the Act, the Secretary shall designate
critical habitat, and revise critical habitat on the basis of the best
scientific data available and after taking into consideration the
economic impact, national security impact, and any other relevant
impact of specifying a particular area as critical habitat. The
Secretary may exclude any particular area from critical habitat if the
benefits of such exclusion outweigh the benefits
[[Page 73828]]
of specifying such area as critical habitat, unless the failure to
designate such area as critical habitat will result in the extinction
of the species. These determinations are made by the Secretary on a
species-by-species and area-by-area basis.
Section 318 of the fiscal year 2004 National Defense Authorization
Act (Pub. L. 108-136) amended the Act by adding a new section
4(a)(3)(B). This provision prohibits designation of critical habitat on
any lands or other geographical areas owned or controlled by the
Department of Defense (DoD), or designated for its use, that are
subject to an INRMP prepared under section 101 of the Sikes Act (16
U.S.C. 670a), if the Secretary determines in writing that such plan
provides a benefit to the species for which critical habitat is
proposed for designation.
The provisions of section 3(5)(A), 4(a)(3), and 4(b)(2) of the Act
are fully considered by us when designating critical habitat. In some
cases, critical habitat may have been designated on lands owned or
controlled by the DOD prior to the 2004 amendments to the Act, or if
otherwise determined to be appropriate. Please see the section
``Application of Section 3(5)(A), Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the Act'' for more information. Any
revisions to designated critical habitat could be considered through
the formal rulemaking process, subject to funding availability.
Public Comments Related to NCCP/HCP Program, Section 7, and Section 404
(42) Comment: One commenter stated that the Ranch Plan, a component
of the draft Orange County Southern Subregion NCCP/HCP is designed to
maximize gene flow for Brodiaea filifolia and that implementation of
the Ranch Plan would not significantly reduce genetic exchange because
of preexisting isolation. The commenter requested their property be
excluded from critical habitat designation for B. filifolia because of
the protections afforded the species under the draft NCCP/HCP.
Our Response: In general, it is our policy to consider excluding
from critical habitat designation HCPs that are approved or are very
close to completion as indicated by the fact that an Environmental
Impact Statement/Environmental Impact Report (EIS/EIR) has already been
prepared and released for public review and comment. We have not yet
released a draft EIS/EIR for the Orange County Southern Subregion NCCP/
HCP for public review and comment; however, we are excluding from final
critical habitat designation the portion of lands within the boundary
of the draft NCCP/HCP that are owned by Rancho Mission Viejo and
identified in the Ranch Plan under section 4(b)(2) of the Act, based on
a recent Settlement Agreement. Please refer to the section
``Application of Section 3(5)(A), Exemption Under Section 4(a)(3), and
Exclusions Under Section 4(b)(2) of the Act'' for more information.
(43) Comment: One commenter stated that the City of San Marcos does
not have an approved HCP and is not likely to have one in the near
future that would warrant exclusion of their lands from critical
habitat under section 4(b)(2) of the Act.
Our Response: We did not exclude any lands within the City of San
Marcos under section 4(b)(2) of the Act; however, some lands in the
City of San Marcos were removed from further consideration as critical
habitat. Please refer to the ``Application of Section 3(5)(A),
Exemption Under Section 4(a)(3), and Exclusions Under Section 4(b)(2)
of the Act'' for more information.
(44) Comment: Three commenters supported our practice of excluding
critical habitat on areas covered by HCPs. One also suggested that we
exclude areas covered under proposed HCPs, noting that failure to do so
would remove incentives for them to participate in these planning
efforts. This commenter also stated that exemptions from critical
habitat should automatically follow approval of an HCP. Another
commenter further stated that designating critical habitat in areas
covered by an HCP would impose economic burdens, invite legal
challenges, and be a disincentive to developing HCPs.
Our Response: It is our policy to exclude from critical habitat
lands containing features essential to the conservation of a federally
listed species that are covered by approved HCPs. Pursuant to section
4(b)(2) of the Act, critical habitat is to be designated or revised
ba