Endangered and Threatened Wildlife and Plants; 90-Day Finding on a Petition To List Usnea longissima in California as Threatened or Endangered, 56937-56938 [E6-15876]
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Federal Register / Vol. 71, No. 188 / Thursday, September 28, 2006 / Proposed Rules
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
Endangered and Threatened Wildlife
and Plants; 90-Day Finding on a
Petition To List Usnea longissima in
California as Threatened or
Endangered
Fish and Wildlife Service,
Interior.
ACTION: Notice of 90-day petition
finding.
cprice-sewell on PROD1PC66 with PROPOSALS
AGENCY:
SUMMARY: We, the U.S. Fish and
Wildlife Service (Service), announce a
90-day finding on a petition to list
Usnea longissima (a lichen) in
California as threatened or endangered
under the Endangered Species Act of
1973, as amended (Act). Based on our
review and evaluation, we find that
there is not substantial scientific or
commercial information to demonstrate
that the California populations of U.
longissima are a discrete and listable
entity under the Act. Therefore, we have
determined that the petition does not
provide substantial information to
indicate that the petitioned action may
be warranted, and we will not be
initiating a further status review of this
species in response to this petition. We
ask the public to submit to us any new
information that becomes available
concerning the status of U. longissima
or threats to it.
DATES: The finding announced in this
document was made on September 28,
2006.
ADDRESSES: The complete supporting
file for this finding is available for
public inspection, by appointment,
during normal business hours at the
Arcata Fish and Wildlife Office, U.S.
Fish and Wildlife Service, 1655
Heindon Road, Arcata, CA 95521. New
information, data, or questions
concerning Usnea longissima may be
submitted to us at any time at the above
address.
FOR FURTHER INFORMATION CONTACT:
Mike Long, Arcata Fish and Wildlife
Office (see ADDRESSES), by telephone at
707–822–7201, or by facsimile to 707–
822–8411. Persons who use a
telecommunications device for the deaf
(TDD) may call the Federal Information
Relay Service (FIRS) at 800–877–8339,
24 hours a day, 7 days a week.
SUPPLEMENTARY INFORMATION:
Background
Section 4(b)(3)(A) of the Act (16
U.S.C. 1531 et seq.) requires that we
make a finding on whether a petition to
VerDate Aug<31>2005
15:43 Sep 27, 2006
Jkt 208001
list, delist, or reclassify a species
presents substantial scientific or
commercial information to indicate that
the petitioned action may be warranted.
We are to base this finding on
information provided in the petition. To
the maximum extent practicable, we are
to make this finding within 90 days of
our receipt of the petition and publish
our notice of this finding promptly in
the Federal Register.
Our standard for substantial
information within the Code of Federal
Regulations (CFR) with regard to a 90day petition finding is ‘‘that amount of
information that would lead a
reasonable person to believe that the
measure proposed in the petition may
be warranted’’ (50 CFR 424.14(b)). If we
find that substantial information was
presented, we are required to promptly
commence a review of the status of the
species.
In making this finding, we relied on
information provided by the petitioner
and our evaluation of that information
in accordance with 50 CFR 424.14(b).
Our process of coming to a 90-day
finding under section 4(b)(3)(A) of the
Act and § 424.14(b) of our regulations is
limited to a determination of whether
the information in the petition meets the
‘‘substantial information’’ threshold.
The factors for listing, delisting, or
reclassifying a species are described in
50 CFR 424.11.
We do not conduct additional
research at this point, nor do we subject
the petition to rigorous critical review.
However, we do check the petitioners
sources and characterizations of
information to determine that the
sources support the characterizations,
and that the sources are published and
peer-reviewed, based on accepted
scientific principles, or otherwise
constitute scientific data.
Previous Federal Action
On April 16, 2000, we received a
petition, dated March 27, 2000, from
Rudolf W. Becking (the petitioner)
requesting that we list Usnea longissima
in California.
On April 27, 2005, we sent a letter to
the petitioner stating that we had
assimilated considerable information on
the distribution of Usnea longissima
and were requesting that the petitioner
contact the Arcata Fish Wildlife Office
to discuss the petition and the need to
list the species. We received no
response to our April 27, 2005, letter
from the petitioner.
Species Information
The genus Usnea was first described
in 1742 (Dillenius 1742). In 1824, it was
placed in the Usneaceae family, and the
PO 00000
Frm 00038
Fmt 4702
Sfmt 4702
56937
species Usnea longissima was described
(Articus 2004, p. 3). Currently, the
genus is classified as a member of the
Parmeliaceae family. U. longissima is
easily distinguishable from other
members of the genus by its long, stringlike growth habit and white central cord
(Pojar and Makinnon 1994, p. 502).
Usnea longissima, commonly called
Methuselah’s Beard or Oldman’s Beard,
is a lichen that resembles hanging
strands of pale yellowish-green hair. A
typical strand of lichen can be from 15
centimeters (6 inches) to 6 meters (19
feet) long. Each strand consists of a
single main elastic strand with
numerous short branchlets (Pojar and
Makinnon 1994, p. 503).
Usnea longissima is typically found
draped over tree branches and shrubs in
well-ventilated, semi-open canopy
forests. This species is not encountered
frequently; however, in areas where
populations are present, they are
abundant. The healthiest populations of
U. longissima are found in old-growth
forests (Pojar and Makinnon 1994, p.
503).
Usnea longissima is an epiphytic (a
plant that grows upon or attached to
another living plant) lichen consisting
of a symbiotic relationship between
fungal and algal organisms. The fungal
part of the lichen (the mycobiont) forms
the structure of the lichen, giving it
shape and a medium for water
absorption. The fungal portion also
provides the lichen with nutrients. The
algal component (the photobiont) is
responsible for providing carbohydrates
to the fungus through the process of
photosynthesis (Vitt et al. 1988, pp.
156–175, 250–251).
In general, lichens reproduce by
producing small propagules (seed-like
parts of the plant) or by dispersal of
fragments from the parent plant. Most of
the reproduction occurs by
fragmentation. Small pieces of lichen
that contain both the fungal and algal
components fall off the parent lichen
and become established somewhere else
in the canopy.
Population Distribution and Trends
Usnea longissima was once a common
circumpolar boreal conifer forest species
(Ahti 1977, pp. 145–181). Currently, U.
longissima has been extirpated from
much of its range in western Europe
(Bennett 1995, pp. 194–196), with the
largest remaining European populations
in Scandinavia, especially in Norway
(Halonen 2000, p 15). The Pacific
Northwest remains a relative stronghold
for the species (Keon 2001, p. 6).
However, U. longissima is also known
to occur in parts of eastern Canada and
E:\FR\FM\28SEP1.SGM
28SEP1
56938
Federal Register / Vol. 71, No. 188 / Thursday, September 28, 2006 / Proposed Rules
cprice-sewell on PROD1PC66 with PROPOSALS
in the northeastern United States
(Halonen 2000, p. 15).
The information presented in the
petition suggests that Usnea longissima
populations are facing increased
pressure in California from several
factors, including habitat loss and
commercial timber harvesting. In the
Coast Range of the Pacific Northwest, U.
longissima seems more limited in
occurrences by its inability to easily
disperse than by the possible lack of
suitable habitat (Keon 2001, p. 92–94).
U. longissima disperses mostly from
small pieces fragmenting from the main
plant and being carried off in the wind,
by an animal, or by simply falling onto
another plant (Pojar and Makinnon
1994, p. 503). This lichen has a short
dispersal distance, usually less than 5
meters (16 feet) (McCune and Geiser
1997, pp. 301, 307, and 353). Therefore,
U. longissima recolonization of second
growth forests may be more dependent
upon proximity to existing U.
longissima populations than on other
habitat characteristics, such as tree age
(Keon and Muir 2002, pp. 233–242).
Review of the Petition
The petition states that Usnea
longissima has been extirpated from
much of its former range in western
Europe primarily due to intensive evenaged logging and acid rain, and that it
is being extirpated in California through
habitat disturbance. The petition
contends that U. longissima is highly
dependent on large, mature trees for
habitat and that logging of old-growth
forest is leading to its extirpation. Our
review of the information present in the
petition suggests that air quality has also
contributed to the extirpation of the
Usnea longissima in some parts of
Europe. The petition requests that the
California populations of U. longissima
be listed under the Act as endangered or
threatened.
However, the petition contains no
information about whether western
Europe or California is a significant
portion of the species’ range. Therefore,
the petition does not provide substantial
information that areas in western
Europe or California constitute a
significant portion of the species’ global
range. The petition also does not request
that we list the species across its range.
To list the species in California alone,
as requested by the petitioner, we would
have to determine that the occurrences
in California constitute a Distinct
Population Segment. The Act restricts
the use of Distinct Population Segments
to vertebrate animal species (16 U.S.C.
1532(16); 61 FR 4722; February 7, 1996).
U. longissima is not a vertebrate animal,
and thus we have no authority to list a
VerDate Aug<31>2005
19:13 Sep 27, 2006
Jkt 208001
distinct population segment of this
species. Therefore, the California
populations of U. longissima are not
considered to be a listable entity
pursuant to the Act and as a result are
ineligible for listing.
Regarding the petitioner’s contention
that U. longissima is dependent on large
mature trees, we note that studies
addressing Usnea longissima
distributions in coastal Oregon forests
(Keon 2001, pp. 92–94; Keon and Muir
2002, pp. 233–242) and reviews of U.
longissima occurrences on Pacific
Lumber Company (PALCO) lands in
northern coastal California (Leppig
2003, pp. 1–3) suggest that U.
longissima occurrences may be more
dependent on the species’ ability to
disperse than on the age of the host
trees. Leppig’s review (2003, p. 2) of U.
longissima on PALCO lands determined
that it occurs on all tree species present
in the stands and is relatively abundant
in younger, 20- to 30-year-old forest
stands. Keon and Muir (2002, pp. 233–
242) found that U. longissima
transplants in young stands grew
hardier than transplants in an old
growth setting. Additionally, our
reviews of PALCO timber harvest plans
suggest that U. longissima is relatively
abundant in watersheds that have been
previously harvested (Leppig 2003, p.
2), suggesting that U. longissima
populations are resilient. In summary,
although Pojar and Makinnon (1994, p.
503) found that the healthiest
populations of U. longissima are in oldgrowth forests, this slow-growing lichen
is not restricted to such an age class. In
addition, contrary to the implications in
the petition, where the species has been
studied in the Pacific Northwest, it
occurs with relative abundance in
younger 20- to 30-year-old forest stands
(Leppig 2003, pp. 1–3) and in
watersheds that have undergone forest
harvests (Leppig 2003, p. 2).
Finding
We reviewed the petition to list Usnea
longissima in California and the
literature cited in the petition, and we
evaluated that information in relation to
other pertinent literature and
information available to us. After this
review and evaluation, we find that
there is not substantial scientific or
commercial information to demonstrate
that the California populations of U.
longissima are a listable entity, and as
a result, we have determined that the
petitioned action is not warranted.
Although we will not be commencing a
status review in response to this
petition, we encourage interested parties
to continue to gather data that will assist
with the conservation of the species.
PO 00000
Frm 00039
Fmt 4702
Sfmt 4702
References Cited
A complete list of all references cited
herein is available upon request from
the Arcata Fish and Wildlife Office (see
ADDRESSES).
Author
The primary authors of this notice are
the staff of the Arcata Fish and Wildlife
Office (see ADDRESSES).
Authority: The authority for this action is
the Endangered Species Act of 1973, as
amended (16 U.S.C. 1531 et seq.).
Dated: September 20, 2006.
Marshall P. Jones, Jr.,
Acting Director, Fish and Wildlife Service.
[FR Doc. E6–15876 Filed 9–27–06; 8:45 am]
BILLING CODE 4310–55–P
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
RIN 1018–AU66
Endangered and Threatened Wildlife
and Plants; 12-Month Finding on a
Petition To Delist the Idaho
Springsnail; 12-Month Finding on a
Petition To List the Jackson Lake
Springsnail, Harney Lake Springsnail,
and Columbia Springsnail; and
Proposed Rule To Remove the Idaho
Springsnail From the List of
Threatened and Endangered Wildlife
Fish and Wildlife Service,
Interior.
ACTION: Notice of two 12-month petition
findings and a proposed rule to delist
the Idaho springsnail (Pyrgulopsis
idahoensis).
AGENCY:
SUMMARY: We, the U.S. Fish and
Wildlife Service (USFWS, Service, or
we), under the Endangered Species Act
of 1973, as amended (Act), announce
combined 12-month findings on a
petition to delist the endangered Idaho
springsnail (Pyrgulopsis idahoensis) and
a petition to list the Jackson Lake
springsnail (P. robusta), Harney Lake
springsnail (P. hendersoni), and
Columbia springsnail (P. species A
(unnamed)). Evidence collected
subsequent to the December 14, 1992,
listing (USFWS 1992, pp. 59244–59527
(57 FR 59244)) of the Idaho springsnail
indicates it no longer constitutes a
distinct species. It is now described as
the Jackson Lake springsnail (P.
robusta), a single taxon, composed of
four previously distinct springsnail
species (Idaho, Jackson Lake, Harney
Lake, and Columbia springsnails), and
therefore we are proposing to remove
E:\FR\FM\28SEP1.SGM
28SEP1
Agencies
[Federal Register Volume 71, Number 188 (Thursday, September 28, 2006)]
[Proposed Rules]
[Pages 56937-56938]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E6-15876]
[[Page 56937]]
-----------------------------------------------------------------------
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
Endangered and Threatened Wildlife and Plants; 90-Day Finding on
a Petition To List Usnea longissima in California as Threatened or
Endangered
AGENCY: Fish and Wildlife Service, Interior.
ACTION: Notice of 90-day petition finding.
-----------------------------------------------------------------------
SUMMARY: We, the U.S. Fish and Wildlife Service (Service), announce a
90-day finding on a petition to list Usnea longissima (a lichen) in
California as threatened or endangered under the Endangered Species Act
of 1973, as amended (Act). Based on our review and evaluation, we find
that there is not substantial scientific or commercial information to
demonstrate that the California populations of U. longissima are a
discrete and listable entity under the Act. Therefore, we have
determined that the petition does not provide substantial information
to indicate that the petitioned action may be warranted, and we will
not be initiating a further status review of this species in response
to this petition. We ask the public to submit to us any new information
that becomes available concerning the status of U. longissima or
threats to it.
DATES: The finding announced in this document was made on September 28,
2006.
ADDRESSES: The complete supporting file for this finding is available
for public inspection, by appointment, during normal business hours at
the Arcata Fish and Wildlife Office, U.S. Fish and Wildlife Service,
1655 Heindon Road, Arcata, CA 95521. New information, data, or
questions concerning Usnea longissima may be submitted to us at any
time at the above address.
FOR FURTHER INFORMATION CONTACT: Mike Long, Arcata Fish and Wildlife
Office (see ADDRESSES), by telephone at 707-822-7201, or by facsimile
to 707-822-8411. Persons who use a telecommunications device for the
deaf (TDD) may call the Federal Information Relay Service (FIRS) at
800-877-8339, 24 hours a day, 7 days a week.
SUPPLEMENTARY INFORMATION:
Background
Section 4(b)(3)(A) of the Act (16 U.S.C. 1531 et seq.) requires
that we make a finding on whether a petition to list, delist, or
reclassify a species presents substantial scientific or commercial
information to indicate that the petitioned action may be warranted. We
are to base this finding on information provided in the petition. To
the maximum extent practicable, we are to make this finding within 90
days of our receipt of the petition and publish our notice of this
finding promptly in the Federal Register.
Our standard for substantial information within the Code of Federal
Regulations (CFR) with regard to a 90-day petition finding is ``that
amount of information that would lead a reasonable person to believe
that the measure proposed in the petition may be warranted'' (50 CFR
424.14(b)). If we find that substantial information was presented, we
are required to promptly commence a review of the status of the
species.
In making this finding, we relied on information provided by the
petitioner and our evaluation of that information in accordance with 50
CFR 424.14(b). Our process of coming to a 90-day finding under section
4(b)(3)(A) of the Act and Sec. 424.14(b) of our regulations is limited
to a determination of whether the information in the petition meets the
``substantial information'' threshold. The factors for listing,
delisting, or reclassifying a species are described in 50 CFR 424.11.
We do not conduct additional research at this point, nor do we
subject the petition to rigorous critical review. However, we do check
the petitioners sources and characterizations of information to
determine that the sources support the characterizations, and that the
sources are published and peer-reviewed, based on accepted scientific
principles, or otherwise constitute scientific data.
Previous Federal Action
On April 16, 2000, we received a petition, dated March 27, 2000,
from Rudolf W. Becking (the petitioner) requesting that we list Usnea
longissima in California.
On April 27, 2005, we sent a letter to the petitioner stating that
we had assimilated considerable information on the distribution of
Usnea longissima and were requesting that the petitioner contact the
Arcata Fish Wildlife Office to discuss the petition and the need to
list the species. We received no response to our April 27, 2005, letter
from the petitioner.
Species Information
The genus Usnea was first described in 1742 (Dillenius 1742). In
1824, it was placed in the Usneaceae family, and the species Usnea
longissima was described (Articus 2004, p. 3). Currently, the genus is
classified as a member of the Parmeliaceae family. U. longissima is
easily distinguishable from other members of the genus by its long,
string-like growth habit and white central cord (Pojar and Makinnon
1994, p. 502).
Usnea longissima, commonly called Methuselah's Beard or Oldman's
Beard, is a lichen that resembles hanging strands of pale yellowish-
green hair. A typical strand of lichen can be from 15 centimeters (6
inches) to 6 meters (19 feet) long. Each strand consists of a single
main elastic strand with numerous short branchlets (Pojar and Makinnon
1994, p. 503).
Usnea longissima is typically found draped over tree branches and
shrubs in well-ventilated, semi-open canopy forests. This species is
not encountered frequently; however, in areas where populations are
present, they are abundant. The healthiest populations of U. longissima
are found in old-growth forests (Pojar and Makinnon 1994, p. 503).
Usnea longissima is an epiphytic (a plant that grows upon or
attached to another living plant) lichen consisting of a symbiotic
relationship between fungal and algal organisms. The fungal part of the
lichen (the mycobiont) forms the structure of the lichen, giving it
shape and a medium for water absorption. The fungal portion also
provides the lichen with nutrients. The algal component (the
photobiont) is responsible for providing carbohydrates to the fungus
through the process of photosynthesis (Vitt et al. 1988, pp. 156-175,
250-251).
In general, lichens reproduce by producing small propagules (seed-
like parts of the plant) or by dispersal of fragments from the parent
plant. Most of the reproduction occurs by fragmentation. Small pieces
of lichen that contain both the fungal and algal components fall off
the parent lichen and become established somewhere else in the canopy.
Population Distribution and Trends
Usnea longissima was once a common circumpolar boreal conifer
forest species (Ahti 1977, pp. 145-181). Currently, U. longissima has
been extirpated from much of its range in western Europe (Bennett 1995,
pp. 194-196), with the largest remaining European populations in
Scandinavia, especially in Norway (Halonen 2000, p 15). The Pacific
Northwest remains a relative stronghold for the species (Keon 2001, p.
6). However, U. longissima is also known to occur in parts of eastern
Canada and
[[Page 56938]]
in the northeastern United States (Halonen 2000, p. 15).
The information presented in the petition suggests that Usnea
longissima populations are facing increased pressure in California from
several factors, including habitat loss and commercial timber
harvesting. In the Coast Range of the Pacific Northwest, U. longissima
seems more limited in occurrences by its inability to easily disperse
than by the possible lack of suitable habitat (Keon 2001, p. 92-94). U.
longissima disperses mostly from small pieces fragmenting from the main
plant and being carried off in the wind, by an animal, or by simply
falling onto another plant (Pojar and Makinnon 1994, p. 503). This
lichen has a short dispersal distance, usually less than 5 meters (16
feet) (McCune and Geiser 1997, pp. 301, 307, and 353). Therefore, U.
longissima recolonization of second growth forests may be more
dependent upon proximity to existing U. longissima populations than on
other habitat characteristics, such as tree age (Keon and Muir 2002,
pp. 233-242).
Review of the Petition
The petition states that Usnea longissima has been extirpated from
much of its former range in western Europe primarily due to intensive
even-aged logging and acid rain, and that it is being extirpated in
California through habitat disturbance. The petition contends that U.
longissima is highly dependent on large, mature trees for habitat and
that logging of old-growth forest is leading to its extirpation. Our
review of the information present in the petition suggests that air
quality has also contributed to the extirpation of the Usnea longissima
in some parts of Europe. The petition requests that the California
populations of U. longissima be listed under the Act as endangered or
threatened.
However, the petition contains no information about whether western
Europe or California is a significant portion of the species' range.
Therefore, the petition does not provide substantial information that
areas in western Europe or California constitute a significant portion
of the species' global range. The petition also does not request that
we list the species across its range. To list the species in California
alone, as requested by the petitioner, we would have to determine that
the occurrences in California constitute a Distinct Population Segment.
The Act restricts the use of Distinct Population Segments to vertebrate
animal species (16 U.S.C. 1532(16); 61 FR 4722; February 7, 1996). U.
longissima is not a vertebrate animal, and thus we have no authority to
list a distinct population segment of this species. Therefore, the
California populations of U. longissima are not considered to be a
listable entity pursuant to the Act and as a result are ineligible for
listing.
Regarding the petitioner's contention that U. longissima is
dependent on large mature trees, we note that studies addressing Usnea
longissima distributions in coastal Oregon forests (Keon 2001, pp. 92-
94; Keon and Muir 2002, pp. 233-242) and reviews of U. longissima
occurrences on Pacific Lumber Company (PALCO) lands in northern coastal
California (Leppig 2003, pp. 1-3) suggest that U. longissima
occurrences may be more dependent on the species' ability to disperse
than on the age of the host trees. Leppig's review (2003, p. 2) of U.
longissima on PALCO lands determined that it occurs on all tree species
present in the stands and is relatively abundant in younger, 20- to 30-
year-old forest stands. Keon and Muir (2002, pp. 233-242) found that U.
longissima transplants in young stands grew hardier than transplants in
an old growth setting. Additionally, our reviews of PALCO timber
harvest plans suggest that U. longissima is relatively abundant in
watersheds that have been previously harvested (Leppig 2003, p. 2),
suggesting that U. longissima populations are resilient. In summary,
although Pojar and Makinnon (1994, p. 503) found that the healthiest
populations of U. longissima are in old-growth forests, this slow-
growing lichen is not restricted to such an age class. In addition,
contrary to the implications in the petition, where the species has
been studied in the Pacific Northwest, it occurs with relative
abundance in younger 20- to 30-year-old forest stands (Leppig 2003, pp.
1-3) and in watersheds that have undergone forest harvests (Leppig
2003, p. 2).
Finding
We reviewed the petition to list Usnea longissima in California and
the literature cited in the petition, and we evaluated that information
in relation to other pertinent literature and information available to
us. After this review and evaluation, we find that there is not
substantial scientific or commercial information to demonstrate that
the California populations of U. longissima are a listable entity, and
as a result, we have determined that the petitioned action is not
warranted. Although we will not be commencing a status review in
response to this petition, we encourage interested parties to continue
to gather data that will assist with the conservation of the species.
References Cited
A complete list of all references cited herein is available upon
request from the Arcata Fish and Wildlife Office (see ADDRESSES).
Author
The primary authors of this notice are the staff of the Arcata Fish
and Wildlife Office (see ADDRESSES).
Authority: The authority for this action is the Endangered
Species Act of 1973, as amended (16 U.S.C. 1531 et seq.).
Dated: September 20, 2006.
Marshall P. Jones, Jr.,
Acting Director, Fish and Wildlife Service.
[FR Doc. E6-15876 Filed 9-27-06; 8:45 am]
BILLING CODE 4310-55-P