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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 Holland’s 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), Goodding’s 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 Swainson’s 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, Botta’s 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)
  • Cooper’s hawk (Accipiter cooperii)
  • Greater sandhill crane (Grus canadensis tabida)
  • Loggerhead shrike (Lanius ludovicianus)
  • Sharp-shinned hawk (Accipiter striatus)
  • Swainson’s 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 state’s 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.
Cooper’s 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 Goodding’s 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

 


Dennis W. Westcot, Project Administrator
San Joaquin River Group
716 Valencia Ave.
Davis, CA 95616-0153
(530) 758-8633
westcot-sjrga@sbcglobal.net

For information regarding this web site, contact the Modesto Irrigation District.