|
Appendix G
Special-Status Species Evaluation ____________________________________________________________________________________________________________
A total of 59
special-status wildlife species and 22 special-status plant species
were considered in the evaluation of the East Yosemite Valley
Utilities Improvement Plan (table G-1). These special-status species
include those listed under the federal Endangered Species Act of
1973, as amended (USFWS 2002); species listed under the California
Endangered Species Act or accorded special status (i.e.,
considered rare or sensitive by the California Department of Fish
and Game); Yosemite National Park rare plants; and plants listed as
rare in California by the California Native Plant Society. The
purpose of this document appendix is to:
§
Evaluate the effects of the proposed action on special-status
species or their critical habitat that are known to be or could be
present within the project area.
§
Determine the need for consultation and conference with the U.S.
Fish and Wildlife Service.
§
Conform to requirements of the Endangered Species Act (19 U.S.C.
1536 (c), 50 CFR 402) and the National Environmental Policy Act (NEPA,
42 U.S.C. 4321 et seq., implemented at 40 CFR Parts 1500-1508).
Each species
in table G-1 was evaluated to determine (1) the known or likely
occurrence of a species or its preferred habitat in the vicinity of
the project area and the possibility of a species or its preferred
habitat types occurring in areas expected to be affected; (2) the
direct physical loss of habitat; (3) the loss of habitat from its
modification; and (4) the effective loss of habitat due to
construction activity or noise. Habitat fragmentation was also
considered. The special-status species are considered further in
this environmental assessment (in Chapters III and IV,
Special-Status Species sections) if actions proposed in the
alternatives could have direct, indirect, or cumulative impacts on
the species.
The National
Park Service has determined that 40 of the 81 special-status species
listed in table G-1 warrant further consideration in the body of
this environmental assessment, including the Wawona riffle beetle,
Mariposa sideband snail, Sierra pygmy grasshopper, northwestern and
southwestern pond turtle, foothill yellow-legged frog, northern
goshawk, oak titmouse, willow flycatcher, harlequin duck,
white-headed woodpecker, California spotted owl, sharp-shinned hawk,
long-eared owl, yellow warbler, great gray owl, a number of
special-status bat species, and a number of special-status plant
species. The remaining 41 special-status species do not occur in the
project area and there would be no direct, indirect, or cumulative
effect on these species from actions proposed in the alternatives.
These species are not evaluated further in this environmental
assessment.
The federal,
state, and National Park Service special-status species listed in
table G-1 are categorized as:
§
Federal endangered: Any species that is in danger of extinction
throughout all or a significant portion of its national range.
§
Federal threatened: Any species that is likely to become an
endangered species within the foreseeable future throughout all or a
significant portion of its national range.
§
Federal species of concern: Any species that may become vulnerable
to extinction on a national level from declining population trends,
limited range, and/or continuing threats (note that this is no
longer an official U.S. Fish and Wildlife Service category, but is
still considered in this document because it contains many species
that could become threatened or endangered).
§
Federal species of local concern: Species of local or regional
concern or conservation significance.
§
Federally proposed: Species officially proposed (in the Federal
Register) for listing as endangered or threatened.
§
Federally delisted: Delisted species, species to be monitored for 5
years.
§
State of California endangered: Any species that is in danger of
extinction throughout all or a significant portion of its range in
the state.
§
State of California threatened: Any species that is likely to become
an endangered species within the foreseeable future throughout all
or a significant portion of its state range.
§
State of California species of special concern: Any species that may
become vulnerable to extinction on a state level from declining
population trends, limited range, and/or continuing threats; could
become threatened or endangered.
§
State of California rare (plants only): A native plant that,
although not currently threatened with extinction, is present in
small numbers throughout its range, such that it may become
endangered if its present environment worsens.
§
Yosemite National Park rare (plants only): Identified by the
National Park Service as rare.
§
California Native Plant Society List 1B: Plants rare, threatened, or
endangered in California and elsewhere.
§
California Native Plant Society List 2: Plants rare, threatened, or
endangered in California, but more common elsewhere.
§
California Native Plant Society List 3: Plants about which we need
more information a review list.
§
California Native Plant Society List 4: Plants of limited
distribution a watch list.
Critical
habitat has not been designated for any federally listed species
that is known or has potential to occur within the project area.
However, critical habitat for the California red-legged frog has
been designated by the United States Fish and Wildlife Service
northwest of the project area within Yosemite National Park (final
rule dated March 13, 2001, Federal Register 66:14625-14674).
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/
CNPS |
Habitat
Type/Occurrence |
Determination |
|
FEDERALLY
LISTED THREATENED OR ENDANGERED SPECIES |
|
FISH |
|
Delta
smelt
Hypomesus
transpacificus |
FT |
CT |
|
This
species occurs only in Suisun Bay and the Sacramento-San Joaquin
estuary (Delta) near San Francisco Bay in California. Though
the species does not occur in Yosemite National Park, the park
contains the headwaters of tributaries that feed into downstream
habitat for the species. |
Removed
from Further Analysis.
This species does not occur within Yosemite National Park. There
is no expected direct, indirect, or cumulative effect on this
species from the proposed action and this species is not
evaluated further. |
|
Central
Valley steelhead
Oncorhynchus mykiss |
FT |
|
|
This
species occurs in the Sacramento-San Joaquin estuary and
tributaries. Though the species does not occur in Yosemite
National Park, the park contains the headwaters of tributaries
that feed into downstream habitat for the species. |
Removed
from Further Analysis.
This species does not occur within Yosemite National Park. There
is no expected direct, indirect, or cumulative effect on this
species from the proposed action and this species is not
evaluated further. |
|
Sacramento
splittail
Pogonichthys macrolepidotus |
FT |
CSC |
|
Habitat
for this species includes tidal fresh and brackish waters of the
Sacramento-San Joaquin Delta, Suisun Bay, tidal marshes in
Suisun, Napa, and Petaluma, and the main stem of the Sacramento
River. Though the species does not occur in Yosemite National
Park, the park contains the headwaters of tributaries that feed
into downstream habitat for the species. |
Removed
from Further Analysis.
This species does not occur within Yosemite National Park. There
is no expected direct, indirect, or cumulative effect on this
species from the proposed action and this species is not
evaluated further. |
|
REPTILES
AND AMPHIBIANS |
|
California
red-legged frog
Rana
aurora draytonii |
FT |
CSC |
|
Found in
quiet pools in permanent streams in mixed conifer zones and
foothills. Prefers riparian deciduous habitat. Many park museum
specimens from one lake (6,000 feet elevation). Once found in
Yosemite Valley, but now apparently extinct due to loss of
habitat and predation by bullfrogs and other species. |
Removed
from Further Analysis.
Not known from the project area. There is no expected direct,
indirect, or cumulative effect on this species from the proposed
action and this species is not evaluated further. |
| |
|
|
|
|
|
|
|
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
FEDERALLY
LISTED THREATENED OR ENDANGERED SPECIES |
|
BIRDS |
|
Bald eagle
Haliaeetus
leucocephalus |
FT |
CE |
|
Forages
over rivers, streams, and lakes. Primarily eats fish, also
carrion, waterbirds, and small mammals. Transient through
Yosemite Valley and El Portal. No bald eagles are nesting in the
park (NPS 1997c). The species was proposed for delisting July 6,
1999. |
Removed
from Further Analysis.
This species is expected as a transient visitor through
Yosemite. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
|
FEDERALLY
LISTED CANDIDATE SPECIES |
|
REPTILES
AND AMPHIBIANS |
|
Yosemite
toad
Bufo
canorus |
FC |
|
|
Restricted
to areas of wet meadows in central Sierra Nevada between
elevations of 6,400 and 11,300 feet. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
|
Mountain
yellow-legged frog
Rana
muscosa |
FC |
CSC |
|
A species
of mountain habitats, occurring between elevations of 4,500 to
over 12,000 feet; found in streams, lakes, and ponds in a
variety of vegetation types. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
|
FEDERALLY LISTED SPECIES OF CONCERN |
|
INVERTEBRATES |
|
Wawona
riffle beetle
Atractelmis wawona |
FSC |
|
|
This
aquatic species is listed due to its limited distribution in the
North and South Forks of the Merced River. Habitat includes
rocks and mossy areas within the river channel. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
| |
|
|
|
|
|
|
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
FEDERALLY LISTED SPECIES OF CONCERN |
|
Merced
Canyon (Yosemite) shoulderband snail
Helminthoglypta allynsmithi |
FSC |
|
|
Found in
rockslide habitat with shade and moisture. Recorded in Merced
River canyon near El Portal. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
|
Keeled
sideband snail
Monadenia
circumcarinata |
FSC |
|
|
Found in
association with steep limestone outcrops and talus slopes. Not
known to occur outside the Tuolumne River canyon (Maciolek
1985). Nearest known locality is Paper Cabin Ridge,
approximately 18.5 miles west of park boundary. |
Removed
from Further Analysis.
Not known from the project area. There is no expected direct,
indirect, or cumulative effect on this species from the proposed
action and this species is not evaluated further. |
|
Mariposa
sideband snail
Monadenia
hillebrandi |
FSC |
|
|
Occurs in
rockslide habitat with shade and moisture. Reported in Yosemite
Valley in the early 1900s. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Boharts
blue butterfly
Philotiella speciosa bohartorum |
FSC |
|
|
An annual
in the buckwheat family (Chorizanthe membrane) is the suspected
preferred forage plant. It is found in association with
serpentine soils. Last recorded in 1970 near Briceburg in the
Merced River canyon. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
|
Sierra
pygmy grasshopper
Tetrix
sierrana |
FSC |
|
|
Often
found in riparian areas, particularly in the spring and early
summer. One record for El Portal (1953). Only other record is
from Madera County. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
FEDERALLY LISTED SPECIES OF CONCERN |
|
FISH |
|
Red Hills
roach
Lavinia symmetricus |
FSC |
CSC |
|
Generally
found in small, warm intermittent streams. Known from Horton
Creek and other small streams near Sonora, California ( Quelvog,
pers. comm.).
|
Removed
from Further Analysis.
Not known from the project area. There is no expected direct,
indirect, or cumulative effect on this species from the proposed
action and this species is not evaluated further. |
|
Longfin
smelt
Spirinchus thaleichthys |
FSC |
CSC |
|
Sloughs,
edges of rivers and bays. General locations: Suisun Bay,
Montezuma Slough, lower reaches of Sacramento and San Joaquin
rivers, and the Delta.
|
Removed
from Further Analysis.
Not known from the project area. There is no expected direct,
indirect, or cumulative effect on this species from the proposed
action and this species is not evaluated further. |
|
REPTILES
AND AMPHIBIANS |
|
Northwestern pond turtle
Clemmys
marmorata marmorata |
FSC |
CSC |
|
Found in
the Sierra Nevada up to 6,000 feet. Has decreased by up to 80%
in numbers, probably due to habitat fragmentation and non-native
predators. Habitat is permanent water in a variety of habitat
types. Recent records include several from Crane Creek in El
Portal and an unconfirmed report in Yosemite Valley in 1999. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Southwestern pond turtle
Clemmys
marmorata pallida |
FSC |
CSC |
|
Found in
the Sierra Nevada up to 6,000 feet. Has decreased by up to 80%
in numbers, probably due to habitat fragmentation and non-native
predators. Habitat is permanent water in a variety of habitat
types. Recent records include several from Crane Creek in El
Portal and an unconfirmed report in Yosemite Valley in 1999. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Mount
Lyell salamander
Hydromantes platycephalus |
FSC |
CSC |
|
Occurs in
massive rock areas between 4,000 and 11,500 feet in elevation,
in rock fissures, seeps, shade, and low-growing plants. Two
records in Yosemite Valley: base of Cathedral Rocks and base of
Bridalveil Fall. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
FEDERALLY LISTED SPECIES OF CONCERN |
|
REPTILES
AND AMPHIBIANS |
|
Foothill
yellow-legged frog
Rana
boylii |
FSC |
CSC |
|
Formerly
abundant, and found up to elevations of 6,000 feet, this species
has virtually disappeared from its range in the Sierra Nevada
from unknown causes. Preferred habitat was rocky streams and wet
meadows. Historical records exist from Yosemite Valley, but none
recent. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Northern
sagebrush lizared
Scenlopous
graciosus graciosus |
FSC |
|
|
Occupies
high elevation habitats, up to 5,500 feet elevation. Prefers
open areas of shrubs within mixed conifer forests (Jeffrey and
sugar pine) and pinyon-juniper woodlands. |
Removed
from Further Analysis.
Not known from the project area. There is no expected direct,
indirect, or cumulative effect on this species from the proposed
action and this species is not evaluated further. |
|
BIRDS |
|
Northern
goshawk
Accipiter
gentilis |
FSC |
CSC |
|
Favors
moderately dense coniferous forests broken by meadows and other
openings, between 5,000 and 9,000 feet elevation. Typically
nests in mature conifer stands near streams. Habitat destruction
in its range has caused population declines. Has been recorded
in the Valley, primarily between November and February. This
species is considered a transient visitor through the Merced
River corridor. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Oak
titmouse
Baeolophus
inornatus |
FSLC |
|
|
Live oaks
and deciduous woodlands. Common in the park at lower elevations. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
FEDERALLY LISTED SPECIES OF CONCERN |
|
BIRDS |
|
Black tern
Chlidonias niger
|
FSC |
CSC |
|
Prefers to
nest in freshwater marshes, wet meadows, and sloughs, such as
Sacramento River delta. Not found in the park (NPS 2003a).
|
Removed
from Further Analysis.
This species does not nest within Yosemite Valley. There is no
expected direct, indirect, or cumulative effect on this species
from the proposed action and this species is not evaluated
further. |
|
American
dipper
Cinclus
mexicanus |
FSLC |
|
|
Permanent
resident throughout most of western United States; along small,
clear streams. Common in the park. |
Removed
from Further Analysis.
This species is common in the park and is removed from further
analysis as a special-status species. However, impacts to this
species are considered as part of the general wildlife resources
analysis. Refer to Chapter III, Affected Environment, for
background data on this species and Chapter IV, Environmental
Consequences, for an analysis of direct, indirect, or cumulative
effects on this species. |
|
Black
swift
Cypseloides niger |
FSC |
CSC |
|
Occurs in
mountainous regions of the western United States and Canada.
Currently, black swifts occur in three widely separated areas:
central Colorado through central Utah; central and southwestern
coastal California; and southern Alaska to northern Washington
and inland to southwestern Alberta, northern Idaho, and
northwestern Montana. Found in Yosemite Valley. |
Removed
from Further Analysis.
This species does not nest within the area to be affected by
construction. There is no expected direct, indirect, or
cumulative effect on this species from the proposed action and
this species is not evaluated further. |
|
Hermit
warbler
Dendroica occidentalis
|
FSC |
|
|
Found in
various forest types. Common associates are subalpine fir,
western white pine, Engelmann spruce, aspen, and larch. This
species is not known to nest within the park. |
Removed
from Further Analysis.
This species is not known to nest within Yosemite Valley. There
is no expected direct, indirect, or cumulative effect on this
species from the proposed action and this species is not
evaluated further. |
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
FEDERALLY LISTED SPECIES OF CONCERN |
|
BIRDS |
|
Willow
flycatcher
Empidonax
trailii
(ssp.
brewsteri) |
FSC
|
CE |
|
Breeds in
mountain meadows and riparian areas from 2,000 to 8,000 feet
elevation in the Sierra Nevada, with lush growth of shrubby
willows. Has disappeared from much of its range, due to habitat
destruction and parasitism from brown-headed cowbirds.
|
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
American
peregrine falcon
Falco
peregrinus anatum |
FD |
CE |
|
Usually
nest on high cliffs near water to search for prey. Three active
nest sites in Yosemite Valley. |
Removed
from Further Analysis.
This species does not nest within the area to be affected by
construction. There is no expected direct, indirect, or
cumulative effect on this species from the proposed action and
this species is not evaluated further. |
|
Harlequin
duck
Histrionicus histrionicus |
FSC |
CSC |
|
Breeds
along large, swift-moving mountain rivers. Was formerly found in
every major watershed in the Sierra Nevada. A pair of harlequin
ducks was observed within the Merced River in 2000, and a pair
successfully nested in Yosemite Valley in 2002 (NPS 2003b). |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Lewis
woodpecker
Melanerpes lewis
|
FSC |
|
|
Occurs in
open oak savannahs, broken deciduous and coniferous habitats.
Breeds locally along eastern slopes of the Coast Ranges, and in
the Sierra Nevada, Warner Mountains, Klamath Mountains, and in
the Cascade Range. |
Removed
from Further Analysis.
This species does not nest within Yosemite Valley. There is no
expected direct, indirect, or cumulative effect on this species
from the proposed action and this species is not evaluated
further. |
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
FEDERALLY LISTED SPECIES OF CONCERN |
|
BIRDS |
|
Long-billed curlew
Numenius americanus |
FSC |
CSC |
|
Breeds in
wet meadow habitat in northeastern California. Preferred winter
habitats include large coastal estuaries, upland herbaceous
areas, and croplands.
|
Removed
from Further Analysis.
This species is expected as a rare transient visitor through
Yosemite Valley. There is no expected direct, indirect, or
cumulative effect on this species from the proposed action and
this species is not evaluated further. |
|
White-headed woodpecker
Picoides albolarvatus |
FLC |
|
|
Occurs in
montane coniferous forests up to lodgepole pine and red fir
habitats in the Sierra Nevada, Cascade, Klamath, Transverse, and
Peninsular Ranges, and Warner Mountains. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Rufous
hummingbird
Selasphorus rufus
|
FSC |
|
|
Found in a
wide variety of habitats that provide nectar-producing flowers.
Uses valley foothill hardwood, valley foothill hardwood-conifer,
riparian, and various chaparral habitats in both northward and
southward migration; montane riparian, aspen, and high mountain
meadows (to tree line and above) used in southward migration. |
Removed
from Further Analysis.
This species does not nest within Yosemite Valley. There is no
expected direct, indirect, or cumulative effect on this species
from the proposed action and this species is not evaluated
further. |
|
Brewers
sparrow
Spizella breweri
|
FSC |
|
|
Breeds in
treeless shrub habitats with moderate canopy, especially in
sagebrush. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
FEDERALLY LISTED SPECIES OF CONCERN |
|
California
spotted owl
Strix
occidentalis occidentalis |
FSC |
CSC |
|
Breeds in
oak and ponderosa pine forests upslope to lower-elevation red
fir forests (up to elevations of 7,600 feet), with mixed conifer
the optimum type. Presence of California black oak in the forest
canopy also enhances habitat suitability. Confirmed sightings in
Yosemite Valley near Happy Isles, Mirror Lake, Yosemite Chapel,
and the base of Cathedral Rocks. Suitable habitat in or near all
the project sites, with the exception of Tioga Pass. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
MAMMALS |
|
Pygmy
rabbit
Brachylagus idahoensis |
FSC |
CSC |
|
Found in
dense stands of big sagebrush, growing in deep loose soils. In
some areas, greasewood provides the dominant shrub for habitat. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
|
Pale
big-eared bat
Corynorhinus townsendii pallescens |
FSC |
CSC |
|
Found in
all habitats up to alpine zone. Requires caves, mines, or
buildings for roosting. Prefers mesic habitats where it gleans
from brush or trees along habitat edges. Recorded at Wildcat
Creek bridge and Mirror Lake (CDFG 2003). |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
FEDERALLY LISTED SPECIES OF CONCERN |
|
MAMMALS |
|
Spotted
bat
Euderma
maculatum |
FSC |
CSC |
|
Rare
throughout its range. Uses crevices in rockfaces for roosting
and reproduction. Forages in a wide variety of habitats,
primarily for moths. Surveys (19921997) in Yosemite located
this species in numerous locations, including Wawona, Crane
Flat, Tuolumne Meadows, and especially Yosemite Valley. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Greater
western mastiff bat
Eumops
perotis californicus |
FSC |
CSC |
|
Found in a
variety of habitats to over 10,000 feet in elevation. Roosts
primarily in crevices in cliff faces and occasionally trees.
Detected most often over meadows and other open areas, but will
also feed above forest canopy, sometimes to high altitudes.
|
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
California
wolverine
Gulo gulo luteus |
FSC |
CT |
|
Found in a
wide variety of mountain habitats. Needs water, caves, logs, or
other cover for denning. No wolverine have been recorded within
California since the 1970s (CDFG 1999). This species is presumed
extirpated from California. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
|
Sierra
Nevada snowshoe hare
Lepus
americanus tahoensis |
FSC |
CSC |
|
Uncommon
resident of upper elevations in the Sierra Nevada. Prefers the
edges of forested habitats, heterogeneous habitats, and areas
with dense understory, particularly in riparian habitats.
|
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
FEDERALLY LISTED SPECIES OF CONCERN |
|
American
(pine) marten
Martes
americana |
FSC |
|
|
Found in
dense, complex coniferous forests with large trees and snags.
Structural complexity near the ground is important for foraging
and protection from predators. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
|
Pacific
fisher
Martes
pennanti pacifica |
FSC |
CSC |
|
Occurs in
coniferous forests and deciduous-riparian habitats with a high
canopy closure, mostly above 6,000 feet elevations. Carnivorous,
but may also eat fruit and fungi. Densities in the central
Sierra Nevada appear to be very low, for unknown reasons; higher
densities in both the northern and southern Sierra Nevada.
Fishers have been seen within the last 10 years near Henness
Ridge and Crane Flat. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
|
Small-footed myotis bat
Myotis
ciliolabrum |
FSC |
|
|
Usually
found below 8,800 feet and in wooded and brushy habitats near
water. Forages among trees and over water. Breeds in colonies in
buildings, caves, and mines. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Long-eared
myotis bat
Myotis
evotis |
FSC |
|
|
Wide range
from coast to high elevations in the Sierra Nevada, in montane
oak woodlands. Roosts primarily in hollow trees, especially
large snags or lightning-scarred live trees. Captured in
Yosemite Valley in 1993. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
FEDERALLY LISTED SPECIES OF CONCERN |
|
Fringed
myotis bat
Myotis
thysanodes |
FSC |
|
|
Found to
elevations of at least 6,400 feet in the Sierra Nevada in
deciduous/mixed conifer
forests.
Feeds over water, in open habitats, and by feeding on insects
from foliage. Roosts in caves, mines, buildings, and trees,
especially large conifer snags. Captured during surveys in
Yosemite Valley in 1993 near Yosemite Creek. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Long-legged myotis bat
Myotis
volans |
FSC |
|
|
Found up
to high elevations in the Sierra Nevada, in montane coniferous
forest habitats. Forages over water, close to tree and cliffs,
and in openings in forests. Roosts primarily in large-diameter
snags. Forms nursery colonies numbering hundreds of individuals,
usually under bark or in hollow trees. Captured in Yosemite
Valley in 1993. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Yuma
myotis bat
Myotis
yumanensis |
FSC |
CSC |
|
Usually
occurs below 8,000 feet elevation. Forages over open, still, or
slow-moving water and above low vegetation in meadows. Roosts in
caves, buildings, or crevices. Nursery colonies of several
thousand individuals may be in caves, mines, or buildings.
Captured during surveys in Yosemite Valley and Wawona in 1993
and 1994. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Sierra
Nevada red fox
Vulpes vulpes necator |
FSC |
CT |
|
Known only
from Kern County from past records on the Kern Plateau. May be
extirpated entirely from the region. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
FEDERALLY LISTED SPECIES OF CONCERN |
|
VEGETATION |
|
Yosemite
woolly-sunflower
Eriophyllum nubigenum |
FSC |
|
--/1B |
Found
within mixed conifer and montane zones in rock crevices and
gravelly ridges in the open. This species is a California
endemic growing in fewer than 20 sites in Mariposa, Madera, and
Tuolumne Counties. Flowering period: May June. Elevation
range: 5500 9000 feet. |
Removed
from Further Analysis.
This species does not occur in the project area. There is no
expected direct, indirect, or cumulative effect on this species
from the proposed action and this species is not evaluated
further. |
|
Short-leaved hulsea
Hulsea
brevifolia |
FLC |
|
--/1B |
This
species is occasional in California and has a limited habitat;
found in dry openings in red fir forest. Flowering period: June
August. Elevation range: 5200 8200 feet. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
|
Yosemite
lewisia
Lewisia
disepala |
FSC |
|
--/1B |
Found
within mixed conifer and montane zones on open domes in shallow,
decomposed granitic sand that becomes desiccated by early
spring. Flowering period: February June. Elevation range: 4900
9200 feet. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
|
Pansy
monkeyflower
Mimulus
pulchellus |
FLC |
|
PR/1B |
Found
within chaparral/oak woodland and mixed conifer zones in moist
meadows and vernally-moist, open, sandy benches and depressions.
Flowering period: May July. Elevation range: 3400 5100 feet. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
FEDERALLY LISTED SPECIES OF CONCERN |
|
VEGETATION |
|
Yosemite
popcorn-flower
Plagiobothrys torreyi
var.
torreyi |
FLC |
|
--/1B |
This
species is endemic to California and is known only from Yosemite
Valley. It occurs in ponderosa pine forests, red fir forests,
lodgepole forests, subalpine forests, as well as meadows and
seeps. Flowering period: June July. Elevation range: 3900
4600 feet. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Parasol (Bolanders)
clover
Trifolium
bolanderi |
FSC |
|
--/1B |
Confined
to wet montane meadows. This species occurs along Glacier Point
Road. Flowering period: June July. Elevation range: 6900
7500 feet. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
|
STATE-LISTED SPECIES, SPECIES OF SPECIAL CONCERN, AND SPECIES OF
LOCAL CONCERN |
|
BIRDS |
|
Coopers
hawk
Accipiter
cooperi |
|
CSC |
|
A hawk of
wooded areas, found up to 9,000 feet in the Sierra Nevada.
Numerous recent records for Yosemite, especially in Yosemite
Valley. Habitat destruction in its range has led to population
declines. Frequently hunts along wooded edges (NPS 1997c).
|
Removed
from Further Analysis.
This species is relatively tolerant of high levels of
disturbance. There is no expected direct, indirect, or
cumulative effect on this species from the proposed action and
this species is not evaluated further. |
|
Sharp-shinned hawk
Accipiter
striatus |
|
CSC |
|
Hunts in
open coniferous forest and edges of meadows and clearings
between 4,000 and 7,000 feet elevation in the Sierra Nevada.
Nest in forests. One 1930 nesting record for Yosemite Valley. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
STATE-LISTED SPECIES, SPECIES OF SPECIAL CONCERN, AND SPECIES OF
LOCAL CONCERN |
|
BIRDS |
|
Golden
eagle
Aquila chrysaetos |
|
CSC |
|
Found in a
wide range of elevations in the park. Needs open terrain for
hunting. Feeds primarily on small mammals. Nests on cliffs and
in large trees in open areas. |
Removed
from Further Analysis.
This species is considered a transient visitor through Yosemite
Valley. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
|
Long-eared
owl
Asio otus |
|
CSC |
|
Requires
riparian or other thickets with small, densely canopied trees
for roosting and nesting. Proximity of this habitat to meadow
edges for hunting also enhances quality. One nesting record in
Yosemite Valley in 1915 (NPS 1997c). |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Yellow
warbler
Dendroica
petechia |
|
CSC |
|
Prefers
riparian woodlands, but also breeds in chaparral, ponderosa
pine, and mixed conifer habitats with substantial amounts of
brush. In recent decades, numbers of breeding pairs have
declined dramatically in many lowland areas of California. A
major cause of this decline has apparently been brown-headed
cowbird parasitism (NPS 1997c). |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Merlin
Falco columbarius |
|
CSC |
|
Occurs
mostly below elevations of 4,000 feet, ranging from annual
grasslands to ponderosa pine and California black oak woodland,
but prefers open country. Feeds primarily on birds. Reduction in
numbers over recent decades may be due to pesticides. This
species has not been reported in the Merced River corridor. |
Removed
from Further Analysis.
This species is believed extirpated from the project area. There
is no expected direct, indirect, or cumulative effect on this
species from the proposed action and this species is not
evaluated further. |
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
STATE-LISTED SPECIES, SPECIES OF SPECIAL CONCERN, AND SPECIES OF
LOCAL CONCERN |
|
BIRDS |
|
Prairie
falcon
Falco
mexicanus |
|
CSC |
|
Primarily
associated with grasslands and meadows where it feeds on small
mammals and birds. Nests on cliffs. Has declined in California
from several probable factors, including nest robbing by humans,
control of prey species, and pesticides. Many records of this
species in alpine areas of Yosemite, but it is also occasionally
seen in Yosemite Valley and Foresta. |
Removed
from Further Analysis.
This species does not nest within the area to be affected by
construction. There is no expected direct, indirect, or
cumulative effect on this species from the proposed action and
this species is not evaluated further. |
|
Great gray
owl
Strix
nebulosa |
|
CSC |
|
Entire
California population of this species is restricted to the
Yosemite region, where it reaches southernmost extent of its
North American range. Breeds in mixed conifer/red fir forests
bordering meadows. Winters in mixed conifer down to blue oak
woodlands. Research suggests that human disturbance could affect
foraging success of this species, which may explain its absence
from the Valley. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
MAMMALS |
|
Pallid bat
Antrozous
pallidus |
|
CSC |
|
Primarily
found below 6,000 feet in elevation, in a variety of habitats,
especially oak, ponderosa pine, and giant sequoia habitats.
Roosts in rock outcrops, caves, and especially hollow trees. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
MAMMALS |
|
Townsends
big-eared bat
Corynorhinus townsendii townsendii |
|
CSC |
|
Found in
all habitats up to alpine zone. Requires caves, mines, or
buildings for roosting. Prefers mesic habitats where it gleans
from brush or trees along habitat edges. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
PARK RARE PLANTS |
|
Sugar
stick
Allotropa
virgata |
|
|
PR/-- |
Confined
to black oak and mixed conifer forest areas. Flowering period:
June August. Elevation range: 3900 8500 feet. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Round-leaved sundew
Drosera
rotundifolia |
|
|
PR/-- |
Confined
to sphagnum bogs. Flowering period: July August. Elevation
range: 4500 7500 feet. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Stream
orchid
Epipactis
gigantea |
|
|
PR/-- |
Restricted
to moist granitic ledges, and planted in landscaped areas.
Flowering period: May July. Elevation range: 3900 6100 feet. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
PARK RARE PLANTS |
|
Fawn-lily
Erythronium purpurascens |
|
|
PR/-- |
Endemic to
the Sierra Nevada, growing along shaded stream and river
corridors. Flowering period: June August. Elevation range:
5900 7100 feet. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
|
Northern
bedstraw
Galium
boreale
ssp.
Septentrionale |
|
|
PR/-- |
Found in
wet lower montane meadows. Flowering period: June August.
Elevation: 3900 feet. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Sierra
laurel
Leucothoe
davisiae |
|
|
PR/-- |
Grows in
wet areas and bogs in acid soil. Flowering period: June
August. Elevation range: 3900 6400 feet. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
False
pimpernel
Lindernia
dubia
var.
anagallidea |
|
|
PR/-- |
Occurs in
wet meadows. Flowering period: July September. Elevation
range: 1600 4900 feet. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
PARK RARE PLANTS |
|
Azure
penstemon
Penstemon
azureus
ssp. angustissimus |
|
|
PR/-- |
Generally
found in moist woodlands and open forests. Flowering period: May
August. Elevation range: 1600 8000 feet. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Phacelia
Phacelia
tanacetifolia |
|
|
PR/-- |
Grows in
moist sandy and gravelly open areas. Flowering period: March
May. Elevation range: 1600 3900 feet. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Wood
saxifrage
Saxifraga
mertensiana |
|
|
PR/-- |
Endemic to
northern and central Sierra Nevada. Grows on mossy rocks and
moist cliffs. Flowering period: June July. Elevation range:
4500 6600 feet. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
Giant
sequoia
Sequoiadendron giganteum |
|
|
PR/-- |
Grows in
three discrete groves in the park, has also been planted in
historic and recent landscaped areas. Elevation range: 5200
6900 feet. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species.
|
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
PARK RARE PLANTS |
|
Ladies
tresses
Spiranthes
porrifolia |
|
|
PR/-- |
Found in
wet meadows. Flowering period: July August. Elevation range:
3600 4300 feet. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
CALIFORNIA NATIVE PLANT SOCIETY RARE PLANTS |
|
Slender
silvermoss
Anomobryum
filiforme |
|
|
--/2 |
Found in
broadleafed upland forest and lower montane coniferous forest.
Elevation range: 300 3300 feet. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
|
Bolander's
bruchia
Bruchia
bolanderi |
|
|
--/2 |
Found in
lower montane coniferous forest, meadows and seeps, and in damp
soils within upper montane coniferous forest. Elevation range:
5600 9200 feet. |
Removed
from Further Analysis.
Suitable habitat for this species is absent from the project
area. There is no expected direct, indirect, or cumulative
effect on this species from the proposed action and this species
is not evaluated further. |
|
Yosemite
tarplant
Jensia
yosemitana |
|
|
--/3 |
Found in
lower montane coniferous forest, meadows and seeps. Flowering
period: May July. Elevation range: 3500 7500 feet. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
|
|
Special-Status Species Considered in this Analysis
|
|
Status |
|
|
|
Species |
USFWS |
State |
Park/ CNPS |
Habitat
Type/Occurrence |
Determination |
|
CALIFORNIA NATIVE PLANT SOCIETY RARE PLANTS |
|
Nuttall's
pondweed
Potamogeton epihydrus
ssp.
nuttallii |
|
|
--/2 |
Found in
marshes and swamps. Flowering period: July August. Elevation
range: 3300 4300 feet. |
Considered
Further in this Analysis.
Suitable habitat for this species occurs within Yosemite Valley.
Refer to Chapter III, Affected Environment, for background data
on this species and Chapter IV, Environmental Consequences, for
an analysis of direct, indirect, or cumulative effects on this
species. |
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|