|
Additional Water
for the San Joaquin River Agreement,
2000 2010 Supplemental EIS/EIR
6. TERRESTRIAL
BIOLOGY
6.1 Affected Environment
This section describes
the existing vegetation and wildlife in San Joaquin
Valley with emphasis on biological communities along
the San Joaquin River and its tributaries. Sensitive
resources such as wetlands and special-status species
are specifically addressed. Information for this
section is primarily derived from the Meeting
Flow Objectives for the San Joaquin River Agreement,
1999-2010, Final Environmental Impact Statement/Environmental
Impact Report (Final EIS/EIR, Reclamation 1999).
6.1.1
Vegetation Types
A wide variety of vegetation
types occur along the margins of the San Joaquin
River and its tributaries. The species composition
and architecture of these riparian vegetation types
are a function of substrate and the hydrology. The
relationship between vegetation and hydrology has
been previously described in detail in the Final
EIS/EIR (Reclamation 1999) and is not repeated here.
The Proposed Project
could release up to 47,000 acre-feet of supplemental
water into the San Joaquin River. This water would
originate from either the Tuolumne River or the
Merced River. These releases would only affect vegetation
within the immediate area of the rivers and are
not expected to have any effects on vegetation growing
outside the riparian corridor. The boundary limiting
the evaluation scope is defined according to the
limits described in the Final EIS/EIR (Reclamation
1999). These limits are defined as the channel area
below the floodplain called the bankfull channel.
Riparian vegetation
types along the San Joaquin, Tuolumne, and Merced
rivers are identified in this section based on Hollands
classifications (Holland 1986). The following riparian
vegetation types are identified:
- Coast and Valley
freshwater marsh
- Great Valley willow
scrub
- Great Valley cottonwood-willow
riparian forest
- Great Valley cottonwood
riparian forest
- Great Valley mixed
riparian forest
- Great Valley oak
riparian forest
- Southern willow
scrub
- Southern cottonwood-willow
riparian forest
- Buttonbush scrub
The Coast and Valley
freshwater marsh community includes most of the
riparian vegetation types dominated by herbaceous
species. Typical species of this vegetation type
include cattail (Typha spp.), bulrush (Scirpus
spp.), duckweed (Lemna spp.), mosquito fern
(Azolla filiculoides), and pondweed (Potamogeton
spp.). Riparian vegetation types dominated by
trees and shrubs are included in the Great Valley
willow scrub, Great Valley cottonwood-willow riparian
forest, Great Valley cottonwood riparian forest,
Great Valley mixed riparian forest, Great Valley
oak riparian forest, southern willow scrub, southern
cottonwood-willow riparian forest, and buttonbush
scrub communities. Typical tree and shrub species
include Fremont cottonwood (Populus fremontii),
arroyo willow (Salix lasiolepis), Gooddings
black willow (Salix gooddingii), narrowleaf
willow (Salix exigua), shining willow (Salix
lucida ssp. lasiandra), box elder (Acer
negundo), Oregon ash (Fraxinus latifolia),
white alder (Alnus rhombifolia), buttonbush
(Cephalanthus occidentalis var. californicus),
and valley oak (Quercus lobata).
6.1.2
Wildlife
Riparian vegetation
types are important breeding, foraging, roosting,
and resting habitat for many birds, reptiles, small
mammals, and amphibians. Representative bird species
include waterfowl associated with the Pacific Flyway
that overwinter in valley wetlands, upland game
birds such as doves, pheasant, quail, and chukar,
and shorebirds such as terns, plovers, sandpipers,
egrets, and gulls. Riparian vegetation provides
nesting and foraging habitat for raptors such as
Swainsons hawks, red-tailed hawks, bald eagles,
prairie falcons, and owls and passerines such as
warblers, blackbirds, sparrows, flycatchers, and
swallows.
Reptiles and amphibians
that utilize riparian vegetation types include turtles,
snakes, frogs, and salamanders. Many of these species
are aquatic or semiaquatic and lay open, nonshelled
eggs in water or very moist areas provided by rotting
logs or dense leaf litter in riparian areas. Many
of reptile and amphibian species depend on riparian
areas for dispersal corridors and linkages between
populations.
A number of mammals
are transient between upland and riparian habitats
along the San Joaquin River and its tributaries.
These species include the red bat, the Brazilian
free-tailed bat, Virginia opossum, Bottas
pocket gopher, raccoon, striped skunk, and bobcat.
Muskrats are abundant in riparian areas, especially
in freshwater marsh communities. Muskrats are mainly
herbivorous and prefer roots and basal stems of
plants but also consume crayfish, mollusks, turtles,
and fish.
6.1.3
Special-Status Species
A number of rare, threatened,
and endangered species were historically associated
with riparian areas along the San Joaquin, Tuolumne,
and Merced rivers. These special-status species
are listed below:
- Valley elderberry
longhorn beetle (Desmocerus californicus dimorphus)
- California red-legged
frog (Rana aurora draytonii)
- Giant garter snake
(Thamnophis couchi gigas)
- Western pond turtle
(Clemmys marmorata)
- Bald eagle (Haliaeetus
leucocephalus)
- Bank swallow (Riparia
riparia)
- California yellow
warbler (Dendroica petechia brewsteri)
- Coopers hawk
(Accipiter cooperii)
- Greater sandhill
crane (Grus canadensis tabida)
- Loggerhead shrike
(Lanius ludovicianus)
- Sharp-shinned hawk
(Accipiter striatus)
- Swainsons
hawk (Buteo swainsoni)
- Western least bittern
(Ixobrychus exilis hesperis)
- White-tailed kite
(Elanus leucurus)
- Willow flycatcher
(Empidonax traillii brewsteri)
- Riparian woodrat
(Neotoma fuscipes riparia)
- Riparian brush rabbit
(Sylvilagus bachmani riparius)
Table 6-1 summarizes
the current status of these species under the federal
and state Endangered Species Acts.
6.2
Environmental Consequences and Mitigation Measures
This section evaluates
and describes potential impacts to riparian vegetation,
associated wildlife species, and terrestrial special-status
species. Mitigation measures are not required because
there are no potentially significant impacts. The
discussion of impact is divided into three sections:
riparian vegetation, wildlife species, and special-status
species.
6.2.1
Key Impact Issues and Evaluation Criteria
Impact issues and evaluation
criteria are based on the California Environmental
Quality Act guidelines for biological resources,
state and federal laws that regulate impacts to
special-status species and wetlands, and are consistent
with the Final EIS/EIR (Reclamation 1999). Impacts
to terrestrial biological resources are assessed
as "significant," "potentially significant,"
"less than significant," and "no
impact."
6.2.1.1 Riparian
Vegetation
Key issues for riparian
vegetation are those that cause a positive or
negative change to riparian vegetation health
or survival. Where possible, impacts of stress
are differentiated from impacts causing mortality
to riparian vegetation. Adverse impacts on riparian
vegetation (including wetlands) are considered
significant if the Proposed Project would:
- Disturb a substantial
portion of the vegetation type within a local
region, and natural or enhanced regeneration could
not restore this vegetation to its preconstruction
condition within 3 to 5 years.
Table
6-1
Special-Status
Wildlife Species that May Occur in the Project Area
| |
Statusa
|
|
|
Species
|
Federal/
State
|
Habitats
|
| Invertebrates |
| Conservancy
fairy shrimp
Branchinecta
conservatio
|
E/--
|
Large,
deep vernal pools in annual grasslands. |
| Longhorn
fairy shrimp
Branchinecta
longiantenna
|
E/--
|
Small,
clear pools in sandstone rock outcrops of
clear to moderately turbid clay- or grass-bottomed
pools. |
| Valley
elderberry longhorn beetle
Desmocerus
californicus
dimorphus
|
T/--
|
Riparian
and oak savanna habitats with elderberry
shrubs; below 2,000 feet elevation. |
| Vernal
pool fairy shrimp
Branchinecta
lynchi
|
T/--
|
Vernal
pools; sandstone rock outcrop pools. |
| Vernal
pool tadpole shrimp
Lepidurus
packardi
|
E/--
|
Vernal
pools; ephemeral stock ponds. |
| Amphibians
and Reptiles |
| California
tiger salamander
Ambystoma
tigrinum californiense
|
C/SSC
|
Small
ponds, lakes, or vernal pools in grasslands
and oak woodlands for larvae; rodent burrows,
rock crevices, or fallen logs for cover
for adults and for summer dormancy. |
| California
red-legged frog
Rana aurora
draytonii
|
T/SSC
|
Permanent
and semipermanent aquatic habitats such
as creeks and coldwater ponds with emergent
and submergent vegetation and riparian species
along the edges; may estivate in rodent
burrows or cracks during dry periods. |
| Giant
garter snake
Thamnophis
couchi gigas
|
T/T
|
Sloughs,
canals, and other small waterways, where
there is a prey base of small fish and amphibians;
requires grassy banks and emergent vegetation
for basking, and areas of high ground protected
from flooding during winter. |
| Western
pond turtle
Clemmys
marmorata
|
--/SSC
|
Permanent
ponds, lakes, streams, and irrigation ditches;
basking sites, such as logs, rocks, mud
banks, or mats of floating vegetation required;
nests constructed in sandy banks or on hillsides
up to 325 feet from water. |
| Birds |
| Aleutian
Canada goose
Branta
canadensis leucopareia
|
T/--
|
Winters
in the San Joaquin Valley; forages on pastures,
harvested fields, and wetlands; roosts on
flooded fields and ponds at night. |
| Bald
eagle
Haliaeetus
leucocephalus
|
T/E
|
Requires
large, old-growth trees or snags in mixed
stands near large bodies of water or free-flowing
rivers with abundant fish. Roosts communally
in winter in dense, sheltered, remote conifer
stands in proximity to feeding areas. |
| American
peregrine falcon
Falco
peregrinus anatum
|
E/E
|
Nests
and roosts on protected ledges of high cliffs,
usually adjacent to lakes, rivers, or marshes
that support large populations of other
bird species. |
| Bank
swallow
Riparia
riparia
|
--/T
|
Nests
in bluffs or banks adjacent to water where
the soil consists of sand or sandy loam
to allow digging; the states largest
breeding populations are along the Sacramento
River, and along the Feather and Lower American
rivers, in the Owens Valley. |
Table
6-1 (continued)
| |
Statusa
|
|
|
Species
|
Federal/
State
|
Habitats
|
| California
yellow warbler
Dendroica
petechia brewsteri
|
--/SSC
|
Nests
and feeds in riparian deciduous habitats;
preferred species include cottonwoods, willows,
and alders. |
| Coopers
hawk
Accipiter
cooperii
|
--/SSC
|
Dense
stands of live oak, riparian deciduous,
or other forest habitats near water used
most frequently. |
| Greater
sandhill crane
Grus canadensis
tabida
|
--/T
|
Summers
in open terrain near shallow lakes or freshwater
marshes; winters in plains and valleys near
bodies of fresh water. |
| Loggerhead
shrike
Lanius
ludovicianus
|
--/SSC
|
Found
in a wide variety of lowland habitats including
valley foothill hardwood, hardwood-conifer,
valley foothill riparian, and pinyon-juniper. |
| Long-billed
curlew
Numenius
americanus
|
--/SSC
|
Breeds
on grazed, mixed-grass and short grass prairies,
and wetlands; feeds in a variety of wetlands,
and flooded or wet fields. |
| Mountain
plover
Charadrius
montanus
|
C/SSC
|
Frequents
open plains below 3,200 feet elevation with
low herbaceous or scattered shrub vegetation;
plowed fields with little vegetation; avoids
high and dense cover. |
| Northern
harrier
Circus
cyaneus
|
--/SSC
|
Frequents
meadows, grasslands, open rangelands, and
wetlands; nests in emergent wetland or along
rivers or lakes; less frequently nests in
grasslands and grain fields. |
| Prairie
falcon
Falco
mexicanus
|
--/SSC
|
Associated
primarily with perennial grasslands, savannas,
rangelands, and some agricultural fields;
uses open terrain for foraging and nests
in adjacent canyons, cliffs, or rock outcrops. |
| Sharp-shinned
hawk
Accipiter
striatus
|
--/SSC
|
Prefers,
but not restricted to, riparian habitats;
forages in openings at edges of woodlands,
brushy pastures, and shorelines where there
is an abundance of migrating birds. |
| Short-eared
owl
Agio flammeus
|
--/SSC
|
Winters
in the Central Valley; usually found in
open areas with few trees, such as grasslands,
prairies, irrigated lands, meadows, and
wetlands. |
| Swainson's
hawk
Buteo
swainsoni
|
--/T
|
Nests
in oaks or cottonwoods in or near riparian
habitats; forages in grasslands, irrigated
pastures, and grain fields. |
| Western
least bittern
Ixobrychus
exilis hesperis
|
--/SSC
|
Nests
in fresh emergent wetlands in the Central
Valley; rests, roosts, and hides in dense
emergent vegetation; often feeds along the
edge of emergent vegetation on the open-water
side. |
| White-tailed
kite
Elanus
leucurus
|
--/P
|
Forages
in agricultural areas and grasslands; uses
trees with dense canopies for cover; nests
in dense oak, willow, or other tree stand. |
| Willow
flycatcher
Empidonax
traillii brewsteri
|
--/E
|
Riparian
areas and large, wet meadows with abundant
willows for breeding; usually occurs in
riparian habitats during migration. |
Table
6-1 (concluded)
| |
Statusa
|
|
|
Species
|
Federal/
State
|
Habitats
|
| Mammals |
| Giant
kangaroo rat
Dipodomys
ingens
|
E/E
|
Restricted
to flat, sparsely vegetated areas with native
annual grassland and shrubland habitats;
requires uncultivated soils consisting of
dry, fine, sandy loams for burrowing. |
| Tipton
kangaroo rat
Dipodomys
nitratoides nitratoides
|
E/E
|
Constructs
burrows in alkali marshes and on plains.
Unable to use cultivated lands. Prefers
areas with scattered woody shrubs such as
saltbush, and a sparse covering of grasses
and forbs. A critical element of its habitat
is slightly elevated terrain where it can
build burrows above the winter and spring
floods. |
| Fresno
kangaroo rat
Dipodomys
nitratoides exilis
|
E/E
|
Uses
sandy loam soils for excavation of burrows
in gently undulating to level terrain in
mildly to moderately alkaline areas. Herbaceous
vegetation with scattered shrubs preferred. |
| Riparian
woodrat
Neotoma
fuscipes riparia
|
E/SSC
|
Prefers
areas with a mixture of trees and shrubs
with moderate canopy and brushy understory.
Requires cavities in trees, snags, or logs
for nesting. In the San Joaquin Valley,
suitable habitat restricted primarily to
riparian areas where trees and brush are
found. Only known from along the San Joaquin,
Stanislaus, and Tuolumne rivers. |
| Riparian
brush rabbit
Sylvilagus
bachmani riparius
|
E/SSC
|
Occupies
dense thickets of riparian shrubs including
wild rose (Rosa sp.), willows (Salix
sp.), and blackberries (Rubus sp.).
Also uses weedy fields adjacent to shrubs.
Currently only known on the lower Stanislaus
River and possibly in the vicinity of the
confluence of the Stanislaus and San Joaquin
rivers. |
| San
Joaquin kit fox
Vulpes
macrotis mutica
|
E/T
|
Saltbush
scrub, valley grassland, oak woodlands,
and freshwater scrub. Principally occurs
in the San Joaquin Valley. |
Notes:
Status
Federal
E = Listed as endangered
under the federal Endangered Species Act
T = Listed as threatened under the federal Endangered
Species Act
PE = Proposed for federal listing as endangered
under the federal Endangered Species Act
C = Candidate for listing under the federal Endangered
Species Act
SC = U.S. Fish and Wildlife Service species of
concern
-- = No status
State
E = Listed as endangered
under the California Endangered Species Act
T = Listed as threatened under the California
Endangered Species Act
SSC = California Department of Fish and Game species
of special concern
P = Fully protected in California
-- = No status
- Result in the long-term
(more-than-5-year) substantial reduction or alteration
of unique, rare, or special concern vegetation
types or natural communities.
- Lead to the expanded
range of existing invasive exotic weed species
or soil pests so that they interfere with successful
revegetation of natural communities.
- Fill or alter a
wetland, resulting in long-term change in hydrology,
soils, or the composition of vegetation.
6.2.1.2 Wildlife
Potential
wildlife impacts would be limited to species that
utilize riparian vegetation types. Changes in
vegetation and associated wildlife habitat may
result in a shift of species presence within the
riparian system. The significance criteria for
evaluation of impacts to wildlife species are:
- Temporary or permanent
removal, filling, grading, or disturbance of
wetlands and riparian vegetation
- Substantial decrease
in the area of important wildlife habitats or
use areas in the San Joaquin, Merced, and Tuolumne
river systems
- Substantial fragmentation
or isolation of wildlife habitats or movement
corridors, especially riparian or wetland habitats
6.2.1.3 Special-Status
Species
Adverse impacts
to listed species are considered significant if
the Proposed Project would result in:
- A reduction in
the number of individual listed plants, fish,
or wildlife
- Long-term or permanent
loss or alteration of habitat important for
one or more listed species
- Temporary loss
or alteration of habitat important for one or
more listed species that could result in increased
mortality or lowered reproductive success
Adverse impacts to
candidate or sensitive species are considered
significant if Project construction or operation
results in the following:
- Direct or indirect
impacts on candidate or sensitive species population,
or habitat that would contribute to or result
in the federal or state listing of the species,
e.g., by substantially reducing species numbers,
or by resulting in the permanent loss of habitat
essential for the continued existence of a species
6.2.2
Environmental Impacts and Mitigation
All identified impacts
are considered to be not significant adverse impacts.
Potential impacts to riparian vegetation, wildlife,
and special-status species are discussed below.
6.2.2.1 Riparian
Vegetation
Potential
impacts to riparian vegetation as a result of
the two release options of the Proposed Project
in comparison to the No Action Alternative are
evaluated below.
No Action Alternative
This alternative
represents the existing hydrology of the Merced,
Tuolumne, or San Joaquin rivers including the
San Joaquin River Agreement (SJRA) flows and existing
riparian vegetation in the Project Area.
Proposed Action
on the Tuolumne River
Release of
supplemental water into the Tuolumne River during
April or May could occur approximately once in
every 10 years based on historical data for the
period 1922 through 1992 (Appendix A). Based on
this same data, supplemental water could need
to be released into the Tuolumne River during
consecutive April and May periods only once every
20 years. During the period of 1922 to 1992, flows
on the San Joaquin River at Vernalis exceeded
the required "double-step" flows approximately
once every 3 to 4 years. Therefore, the proposed
supplemental releases would not substantially
change the existing hydrologic parameters for
maintenance and establishment of riparian vegetation
along the Tuolumne River. It is possible that
higher flows during this period may promote dispersal
and germination of seeds for some riparian plant
species that disperse seeds during this period
such as Fremont cottonwood, Arroyo willow, and
Gooddings black willow.
Releases of supplemental
water from the Tuolumne River would not cause
a significant adverse impact to riparian vegetation
along the Tuolumne or San Joaquin rivers. To the
extent that supplemental flows enhance the establishment
and survival of riparian plant species, the Proposed
Project may have a minor beneficial impact on
riparian vegetation along the Tuolumne and San
Joaquin rivers.
Proposed Action
on the Merced River
Impacts to
riparian vegetation would be the same as those
described for the Tuolumne River. Supplemental
releases to the Merced River are not likely to
cause a significant adverse impact to riparian
vegetation along the Merced or San Joaquin rivers.
To the extent that supplemental flows enhance
the establishment and survival of riparian plant
species, the Proposed Project may have a minor
beneficial impact on riparian vegetation along
the Merced and San Joaquin rivers.
6.2.2.2 Wildlife
Potential
impacts to wildlife are discussed below.
No Action Alternative
This alternative
would not alter the existing riparian wildlife
habitats of the Merced, Tuolumne, or San Joaquin
rivers.
Proposed Action
on the Tuolumne River
As discussed
above for riparian vegetation, supplemental water
released from the Tuolumne River would not have
a significant impact on riparian vegetation. Therefore,
this alternative would not impact wildlife species
that utilize riparian habitats along the San Joaquin
River or the Tuolumne River.
Proposed Action
on the Merced River
As discussed
above for the Tuolumne River, supplemental water
released from the Merced River would not have
a significant impact on riparian vegetation. Therefore,
this alternative would not impact wildlife species
that utilize riparian habitats along the San Joaquin
or Merced rivers.
6.2.2.3 Special-Status
Species
Several special-status
plants and animals used riparian habitats along
the lower San Joaquin and tributary rivers such
as the Tuolumne, Stanislaus, and Merced rivers.
Potential impacts to these special-status species
are evaluated below.
No Action Alternative
The No Action
Alternative represents existing conditions with
the SJRA flows for terrestrial special-status
species in the Project Area.
Proposed Action
on the Tuolumne River
Releasing
supplemental water from the Tuolumne River would
result in higher peak flows in April and/or May
approximately 1 out of every 10 years (Appendix
A). Historic data for the San Joaquin River between
1922 and 1992 demonstrate that the river has typically
experienced even higher flows, greater than the
"double-step" supplemental releases
proposed under this alternative. Therefore, it
is not likely that this alternative would have
a significant adverse impact on special-status
species that use riparian habitats along the Tuolumne
and San Joaquin rivers.
Proposed Action
on the Merced River
This alternative
is not likely to have a significant adverse impact
on special-status species that use riparian habitats
along the Merced or San Joaquin rivers. This conclusion
is based on the historic hydrologic data previously
discussed for the Tuolumne River.
6.2.3
Impact Summary and Mitigation of Impacts
The Proposed Project
on either the Tuolumne or Merced rivers is not likely
to impact riparian vegetation, wildlife, or terrestrial
special-status species. Therefore, no mitigation
is proposed.
Draft SEIS/EIR
CH6 |
December 20, 2000
|
|