|
Table B-1
Special-Status Species Considered in this Analysis |
|
Species |
Statusa |
Habitat Type/Occurrence |
Determination |
|
USFWS |
State |
Park |
|
Federally Listed Threatened or
Endangered Species |
|
Fish |
|
Delta smelt
Hypomesus transpacificus |
FT |
|
|
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 local setting or cumulative effect on this species from the
proposed action and this species is not evaluated further. |
|
Sacramento splittail
Pogonichthys macrolepidotus |
FT |
|
|
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 local setting 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 local setting 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. The
only recent records for Yosemite come from a lake at 6,000 feet in
elevation in the northern portion of the park. Surveys at this
location within the last five years have found no red-legged frogs
(Knapp 2001). |
Removed from Further Analysis. There
is no expected local setting or cumulative effect on this species
from the proposed action and this species is not evaluated further. |
|
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 1997). The species was proposed for delisting 7/6/99. |
Considered Further in this Analysis. This
species may be a transient visitor to the Lower Yosemite Fall area. |
|
Federal Species of Concern |
|
Invertebrates |
|
Wawona riffle beetle
Atractelmis wawona |
FC |
|
|
This aquatic species has a 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 the Yosemite Creek drainage. |
|
Yosemite sideband snail
Helminthoglypta allynsmithi |
FC |
|
|
Found in rockslide habitat with shade and
moisture. This species is associated with relatively stable rocky
areas. |
Removed from Further Analysis.
Suitable habitat for this species is absent from the project area.
There is no expected local setting or cumulative effect on this
species from the proposed action and this species is not evaluated
further. |
|
Indian Yosemite snail
Monadenia hillebrandi yosemitensis |
FC |
|
|
Rockslide areas may be necessary for shelter. This
species is associated with relatively stable rocky areas. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Sierra pygmy grasshopper
Tetrix sierrana |
FC |
|
|
Pygmy grasshoppers are often found in riparian
areas, particularly in the spring and early summer. One record for
El Portal (1953; NPS 2001). Only other record is from Madera County.
Occurs in upland and riparian habitats. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Bohart’s blue butterfly
Philotiella speciosa bohartorum |
FC |
|
|
The host plant for this species is found in
association with serpentine soils. No host plants or serpentine
soils are found in the Lower Yosemite Fall Project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Reptiles and Amphibians |
|
Limestone salamander
Hydromantes brunus |
FC |
CT |
|
Very limited distribution along Merced River and
its tributaries between 800 and 2,500 feet in elevation, usually in
association with limestone outcrops. This species has limited
distribution along the Merced River outside Yosemite National Park. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Mount Lyell salamander
Hydromantes platycephalus |
FC |
CSC |
|
Occurs in massive rock areas between 4,000 and
11,500 feet in elevation, in rock fissures, seeps, shade, and
low-growing plants. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Foothill yellow-legged frog
Rana boylei |
FC |
CSC |
|
Formerly abundant and found up to 6,000 feet in
elevation, this species has virtually disappeared from its range in
the Sierra Nevada from unknown causes. Preferred habitat was rocky
streams and wet meadows. |
Removed from Further Analysis. There
is no expected local setting or cumulative effect on this species
from the proposed action and this species is not evaluated further. |
|
Northwestern pond turtle
Clemys marmorata marmorata |
FC |
CSC |
|
Found in the Sierra Nevada up to 6,000 feet in
elevation, this species has decreased in numbers by up to 80%,
probably due to habitat fragmentation and non-native predators.
Habitat is permanent, slow-moving water in a variety of habitat
types. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Southwestern pond turtle
Clemys marmorata pallida |
FC |
CSC |
|
Found in the Sierra Nevada up to 6,000 feet in
elevation, this species has decreased in numbers by up to 80%,
probably due to habitat fragmentation and non-native predators.
Habitat is permanent, slow-moving water in a variety of habitat
types. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Birds |
|
Harlequin duck
Histrionicus histrionicus |
FC |
CSC |
|
Breeds along large, swift-moving mountain rivers.
Was formerly found in every major watershed in the Sierra, but has
disappeared. Formerly nested in Yosemite Valley (NPS 1997). A pair
of harlequin ducks was observed within the Merced River in 2000. No
recent nesting harlequin duck have been documented within Yosemite
National Park. Nesting pairs of this species are presumed extirpated
from Yosemite National Park. |
Considered Further in this Analysis. Refer
to Chapter 3 for background data on this species and Chapter 4 for
an analysis of local setting or cumulative effects on this species. |
|
Northern goshawk
Accipiter gentilis |
FC |
CSC |
|
Favors moderately dense coniferous forests broken
by meadows and other openings, between 5,000 and 9,000 feet in
elevation. Typically nests in mature conifer stands near streams.
Habitat destruction in its range has caused declines in population.
Records exist for Yosemite Valley, primarily between November and
February. |
Removed from Further Analysis. This
species is considered a transient visitor through the greater
project area. There is no expected local setting or cumulative
effect on this species from the proposed action and this species is
not evaluated further. |
|
California spotted owl
Strix occidentalis occidentalis |
FC |
CSC |
|
Breeds from oak and ponderosa pine forests upslope
to lower-elevation red fir forests up to 7,600 feet, with mixed
conifer the optimum type. Presence of black oak in the forest canopy
also enhances habitat suitability. |
Removed from Further Analysis. The
California spotted owl was not found in the local setting and
project area for the Lower Yosemite Fall Project during recent
surveys (Steger 2000). |
|
Mammals |
|
Spotted bat
Euderma maculatum |
FC |
CSC |
|
Rare throughout range. Uses crevices in rock faces
for roosting and reproduction. Forages in a wide variety of
habitats, primarily for moths. |
Considered Further in this Analysis. Suitable
habitat for this species is found in the Lower Yosemite Fall area. |
|
Small-footed myotis bat
Myotis ciliolabrum |
FC |
|
|
Usually found above 6,000 feet and in wooded and
brushy habitats near water. Forages among trees and over water.
Breeds in colonies in buildings, caves, and mines (NPS 1997). |
Considered Further in this Analysis. Suitable
habitat for this species is found in the Lower Yosemite Fall area. |
|
Long-eared myotis bat
Myotis evotis |
FC |
|
|
Wide range, from coast to high Sierra Nevada, in
montane oak woodlands. Roosts primarily in hollow trees, especially
large snags or lightning-scarred, live trees. Presence in Lower
Yosemite Fall area confirmed in 1993 (Pierson & Rainey 1993). |
Considered Further in this Analysis. Suitable
habitat for this species is found in the Lower Yosemite Fall area. |
|
Fringed myotis bat
Myotis thysanodes |
FC |
|
|
Found to at least 6,400 feet in the Sierra Nevada,
in deciduous/mixed conifer forests. Roosts in caves, mines,
buildings, and trees, especially large conifer snags. Confirmed in
Lower Yosemite Fall area in 1993 (Pierson & Rainey 1993). |
Considered Further in this Analysis. Suitable
habitat for this species is found in the Lower Yosemite Fall area. |
|
Long-legged myotis bat
Myotis volans |
FC |
|
|
Found up to high elevations in the Sierra Nevada,
in montane coniferous forest habitats. Forages over water, close to
trees and cliffs, and in openings in forests. Roosts primarily in
large-diameter snags. Not recorded in recent surveys, though
suitable habitat is found in the Lower Yosemite Fall area. |
Considered Further in this Analysis. Suitable
habitat for this species is found in the Lower Yosemite Fall area. |
|
Yuma myotis bat
Myotis yumanensis |
FC |
|
|
Usually occurs below 8,000 feet in elevation.
Forages over open, still, or slow-moving water and above low
vegetation in meadows. Roosts in buildings, caves, or crevices.
Confirmed in Lower Yosemite Fall area in 1993 and 1995 surveys
(Pierson & Rainey 1993, 1995). |
Considered Further in this Analysis. Suitable
habitat for this species is found in the Lower Yosemite Fall area. |
|
Greater western mastiff bat
Eumops perotis californicus |
FC |
|
|
Found in a variety of habitats to over 8,000 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 (1,000 feet). A substantial population is found in
Yosemite Valley (Pierson & Rainey 1995). |
Considered Further in this Analysis. Suitable
habitat for this species is found in the Lower Yosemite Fall area. |
|
Vegetation |
|
Congdon’s lomatium
Lomatium congdonii |
FC |
|
|
Restricted to serpentine and metamorphic soils in
canyon live oak woodlands. No serpentine or metamorphic soils
present in the project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
State-Listed Special-Status Species
and Species of Special 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 the greater
project area. There is no expected local setting or cumulative
effect on this species from the proposed action and this species is
not evaluated further. |
|
Cooper’s 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 1997). |
Removed from Further Analysis. There
is no expected local setting 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 in elevation in
the Sierra Nevada. Nests in forests. One old (1930) nesting record
for Yosemite Valley (NPS 1997). |
Removed from Further Analysis. There
is no expected local setting or cumulative effect on this species
from the proposed action and this species is not evaluated further. |
|
Prairie falcon
Falco mexicanus |
|
CSC |
|
Primarily associated with open areas such as
grasslands and meadows, where it feeds on small mammals and birds.
Nests on cliffs. Numbers have declined in California due to several
probable factors, including nest robbing by humans, control of prey
species, and pesticides. Many records of this species in alpine
areas of Yosemite National Park and occasionally seen in Yosemite
Valley. |
Removed from Further Analysis. This
species is considered a transient visitor through the greater
project area. There is no expected local setting or cumulative
effect on this species from the proposed action and this species is
not evaluated further. |
|
Peregrine falcon
Falco peregrinus anatum |
FD |
CE |
|
Usually nests on high cliffs near water to search
for prey. The species was formally delisted 8/25/99. |
Considered Further in this Analysis. Suitable
habitat for this species occurs within the Lower Yosemite Fall area. |
|
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 1997). |
Removed from Further Analysis. This
species does not nest within the project area. There is no expected
local setting or cumulative effect on this species from the proposed
action and this species is not evaluated further. |
|
Great gray owl
Strix nebulosa |
|
CE |
|
The 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
Yosemite Valley, and raises concern about actions that may increase
human disturbance on great gray owl habitat. |
Removed from Further Analysis. This
species does not nest within the project area. There is no expected
local setting or cumulative effect on this species from the proposed
action and this species is not evaluated further. |
|
Willow flycatcher
Empidonax traillii |
|
CE |
|
Breeds in mountain meadows and riparian areas from
2,000 to 8,000 feet in 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. The project area is devoid of lush riparian habitat
necessary to support this species. |
Removed from Further Analysis. This
species does not nest within the project area. There is no expected
local setting or cumulative effect on this species from the proposed
action and this species is not evaluated further. |
|
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 1997). |
Removed from Further Analysis. This
species does not nest within the project area. There is no expected
local setting or cumulative effect on this species from the proposed
action and this species is not evaluated further. |
|
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. Confirmed in Lower Yosemite Fall area (Pierson
& Rainey 1995). |
Considered
Further in this Analysis. Suitable habitat
for this species is found in the Lower Yosemite Fall area. |
|
Pale big-eared bat
Corynorhinus townsendii pallescens |
|
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 1999). |
Considered Further in this Analysis. Suitable
habitat for this species is found in the Lower Yosemite Fall area. |
|
Townsend’s 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. Not
confirmed in Lower Yosemite Fall area during recent surveys, but
suitable habitat is present. |
Considered Further in this Analysis. Suitable
habitat for this species is found in the Lower Yosemite Fall area. |
|
Vegetation |
|
Congdon’s lewisia
Lewisia congdonii |
|
R |
|
Grows on moist, exposed, metamorphic rock faces
and slopes in chaparral and mixed conifer forest. Metamorphic soils
are not present in the Lower Yosemite Fall Project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Park Rare Species |
|
Vegetation |
|
Sugar stick
Allotropa virgata |
|
|
PR |
Confined to black oak and mixed conifer forest
areas. Not present in project area. |
Removed from Further Analysis. There
is no expected local setting or cumulative effect on this species
from the proposed action and this species is not evaluated further. |
|
Big-scale balsamroot
Balsamorhiza macrolepis
var. macrolepis |
|
|
PR |
Valley and foothill grassland and woodland
communities. Often associated with serpentine soils. Not present in
project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Sedge
Carex albonigra |
|
|
PR |
Locally rare alpine species. Not present in
project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Congdon’s sedge
Carex congdonii |
|
|
PR |
Uncommon high-elevation species. Not present in
project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Indian paintbrush
Castilleja foliolosa |
|
|
PR |
Found on dry, open, rocky slopes on the edge of
chaparral areas. Not present in project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Child’s blue-eyed Mary
Collinsia childii |
|
|
PR |
Endemic to central and southern Sierra Nevada,
reaching the northern extent of its range in Mariposa County. Occurs
on shaded slopes and in open oak and mixed coniferous woodlands. Not
present in project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Collinsia
Collinsia linearis |
|
|
PR |
Restricted to dry, metamorphic rock outcrops along
the metamorphic-granitic contact zone. Not present in project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Stream orchid
Epipactis gigantea |
|
|
PR |
Restricted to moist granitic ledges, and planted
in landscaped areas. Not present in project area. |
Removed from Further Analysis. There
is no expected local setting or cumulative effect on this species
from the proposed action and this species is not evaluated further. |
|
Fawn-lily
Erythronium purpurascens |
|
|
PR |
Endemic to the Sierra Nevada, growing along shaded
stream and river corridors. Not present in project area. |
Removed from Further Analysis. There
is no expected local setting or cumulative effect on this species
from the proposed action and this species is not evaluated further.
|
|
Boreal bedstraw
Galium boreale ssp.
septentrionale |
|
|
PR |
Found in wet lower montane meadows. Not present in
project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Pitcher sage
Lepechinia calycina |
|
|
PR |
Found on rocky slopes within chaparral and canyon
live oak woodlands. Not present in project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Sierra laurel
Leucothoe davisiae |
|
|
PR |
Grows in wet areas and bogs in acid soil. Not
present in project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
False pimpernel
Lindernia dubia var.
anagallidea |
|
|
PR |
Found in wet meadows. Not present in project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Congdon’s monkeyflower
Mimulus congdonii |
|
|
PR |
Found in granitic soils in disturbed areas, seeps,
runoff areas on slopes. Not present in project area. |
Removed from Further Analysis. There
is no expected local setting or cumulative effect on this species
from the proposed action and this species is not evaluated further. |
|
Palmer’s monkeyflower
Mimulus palmeri |
|
|
PR |
Restricted to damp, shaded slopes under canyon
live oaks. Not present in project area. |
Removed from Further Analysis. There
is no expected local setting or cumulative effect on this species
from the proposed action and this species is not evaluated further. |
|
Azure penstemon
Penstemon azureus ssp.
angustissimus |
|
|
PR |
Generally found in moist woodlands and open
forests. Not present in project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Phacelia
Phacelia platyloba |
|
|
PR |
Found in gravelly or rocky soils in chaparral and
canyon live oak woodland. Not present in project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Phacelia
Phacelia tanacetifolia |
|
|
PR |
Grows in moist sandy and gravelly open areas. Not
present in project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Wood saxifrage
Saxifraga mertensiana |
|
|
PR |
Endemic to northern and central Sierra Nevada.
Grows on mossy rocks and moist cliffs. Not present in project area. |
Removed from Further Analysis. Suitable
habitat for this species is absent from the project area. There is
no expected local setting or cumulative effect on this species from
the proposed action and this species is not evaluated further. |
|
Ladies’ tresses
Spiranthes porrifolia |
|
|
PR |
Found in wet meadows. Not present in project area. |
Removed from Further Analysis. There
is no expected local setting or cumulative effect on this species
from the proposed action and this species is not evaluated further. |