Wildlife of Riparian and Wetland Areas
Although riparian vegetation makes up just a small
fraction of the total land area in California, wildlife
seek food and shelter there more often than any other
habitat type (FISRWG 1998). Over 225 species of birds,
mammals, reptiles, and amphibians depend on stream
corridors for food, water, shade, shelter, nesting,
and migratory pathways (RHJV 2000). Streams and stream
corridors act as the circulatory system of the Earth's
surface, sustaining the life of many species.
Human activities such as flood control, agriculture,
sand and gravel extraction, transportation routes,
and urbanization have contributed to the loss of over
95 percent of the riparian habitat present in California in
the mid-1800s (RHJV 2000). The sensitivity of animal
communities to vegetative communities is well-recognized
(FISRWG 1998), and with the loss of riparian habitat there has
been a corresponding reduction in associated animal populations.
Consequently, many riparian-dependant animal species are now
listed as species of concern, threatened, or endangered. In San
Mateo and Santa Cruz Counties, there are 13
special
status species that occur within riparian or
wetland habitats.
To get an accurate estimate of the wildlife species
that depend on a single watershed or stream requires
an in-depth biological survey involving many hours
of careful observation in different locations along
the stream corridor during both day and night and in
all seasons of the year. Unfortunately, surveys with
this level of detail can take more time and money than
is usually available, but it is possible to use prior
research to predict the species present based on the
habitat within a given area. The California Department
of Fish and Game (CDFG) has developed a computer database
program called the California Wildlife Habitat Relationships
(CWHR, Version 8.0) that includes all of the known
terrestrial vertebrate taxa in California and their
associated habitats (visit
the CWHR
Web site for more information). This database consists
of predictive models that can produce several types of reports
listing wildlife species that are expected to occur in a given
location and set of habitat conditions. According
to the database, there are approximately 200 terrestrial vertebrate
species
that depend on the riparian and wetland
habitats (riverine,
valley
foothill riparian, montane
riparian, estuarine, saline
emergent wetland, freshwater
emergent wetland, and redwood)
found in San Mateo and Santa Cruz Counties. There are also many
fish species in addition to salmonids that make their home in
riparian streams of these areas. Common species of the follwing
animals are discussed here:
Mammals
Of the 502 recent native species and subspecies of land mammals
in California (Hall 1981), approximately 25 percent (133 taxa) are limited
to or largely dependent upon riparian and other wetland communities
(Williams and Kilburn 1984). No other general type of habitat
is as important to mammals as riparian and wetland communities.
The combination of cover, water and food resources makes riparian
habitat desirable for many species that use multiple habitat
types including mule deer, coyote, and bobcats. Other mammals
– such as ringtail, common muskrat, and raccoon – are
dependant upon riparian habitat for at least part of their range
(FISRWG 1998). Riparian habitat also provides dense cover for
roosts, water, and abundant insect populations required by many
bat species. The watersheds in San Mateo and Santa Cruz Counties
support twelve bat species – all
insectivorous – which help to control the mosquito and other
biting insect populations. Populations of mammalian species dependent
upon freshwater and tidal riparian wetland communities have dramatically
declined in nearly every region within California (Williams and
Kilburn 1984). As riparian corridor width is reduced and removed,
the habitat becomes fragmented and no longer provides a migration
corridor. This reduced habitat cannot support the number or diversity
of mammal species that is supported by a healthy system. For
a complete list of results from the CWHR database, see the Mammals
of San Mateo and Santa Cruz Counties Table.
Birds
Riparian zones have been identified as the most important habitats
for landbird species in California (RHJV 2000). The structural
complexity and species diversity of riparian corridors provides
habitat required for nesting, sheltering, and foraging. Insect
production is high within the riparian corridor, providing a
rich food source for insectivores such as vireos, warblers, swallows,
wrens, and flycatchers. Riparian forest trees such as box elder,
big-leaf maple, and birch are highly productive, producing food
resources for seed feeders such as grosbeak, finches, and sparrows.
Migrating species such as the warbling vireo – a neo-tropic
species that travels from Central America to nesting areas along
California's Central Coast – use riparian corridors to
rest and feed during their annual migration. Additionally, coastal
riparian corridors are the nesting destination for some bird
species. Both resident and migrant species nest within riparian
vegetation. Cavity-nesting species such as owls, woodpeckers,
and ducks may require a special habitat component – standing
dead trees (snags) – to provide appropriate nesting sites.
Although snags may be considered unsightly and dangerous, this
dead wood creates a unique habitat necessary for nesting, while
providing a rich food source for insectivores. Soquel Demonstration
Forest is currently examining the effectiveness of creating snags
within the Soquel
Creek watershed to
create habitat. Finally, water resources within riparian systems
provide habitat and feeding opportunities for piscivorous and
aquatic feeding bird species, such as osprey, herons, and ducks.
For a complete list of results from the CWHR database, see the
Birds
of San Mateo and Santa Cruz Counties Table.
Amphibians and Reptiles
In northern California, approximately 50 percent of both reptiles and
amphibians prefer riparian or aquatic habitats (Raedeke et al.
1988). Nearly all amphibians (salamanders, toads, and frogs)
depend on aquatic habitat for reproduction and over wintering
(FISRWG 1998). Many reptiles are functionally tied to riparian
and wetland areas and some are indicators of riparian ecosystem
health. While less restricted by the presence of water, many
reptiles are found primarily in stream corridors and riparian
habitats. For a complete list of results from the CWHR database,
see the Amphibians of San Mateo and Santa Cruz Counties Table and
Reptiles of San Mateo and Santa Cruz Counties Table.
Fish
While riparian habitat supports a wide variety of animals, the streams also provide important habitat. The stream environment has many habitat types that appeal to a variety of fish such as deep pools for resting, shallow riffles for foraging, and lagoon and estuary areas for nursery habitat.
Unlike salmonids and other anadromous fishes, which can alter
their physiology to live in both salt and fresh water during
certain life stages, most fish species are adapted to a single
habitat type. Freshwater habitats support different fish species
than are observed in brackish and saltwater estuary habitats.
Common native freshwater fish species in coastal streams of San
Mateo and Santa Cruz include prickly sculpin (Cottus asper),
coastrange sculpin (Cottus aleuticus), Sacramento sucker
(Catostomus occidentalis) and threespine stickleback
(Gasterosteus aculeatus) – a freshwater
or anadromous species (Conrad et al. 2003, SH&G et al. 2002).
Salmonids, such as steelhead trout (Oncorhynchus mykiss),
spawn in many coastal streams in San Mateo and Santa Cruz Counties,
while coho salmon (O. kisutch) maintain populations
in San Vicente, Waddell, Gazos, and Scott Creeks (see the State
of Fisheries section
for more information). Pacific lamprey (Lampetra tridentate) – an
anadromous fish with a lifecycle similar to salmonids – also
returns to coastal streams to spawn and has been observed in
the San Lorenzo River (SH&G et al. 2002). In addition, there
are many marine fish that use the estuary as nursery grounds.
Native coastal estuary and lagoon fish species include Pacific
staghorn sculpin (Leptocottus armatus), starry flounder
(Platichthys
stellatus), and topsmelt (Atherinops affinis) (Conrad
et al. 2003, SH&G et al. 2002).
Exotic fish species can also be found in coastal streams due to introduction as gamefish, mosquito control, or accidental release. Non-native large-mouth bass, green sunfish, and mosquitofish can be found in stream systems in San Mateo and Santa Cruz Counties (Conrad et al. 2003, SH&G et al. 2002) and yellow-fin goby have been observed in the San Lorenzo Lagoon (SH&G et al. 2002).
Streams flowing into San Francisco Bay have a wide variety of both
native and non-native species. With the exception of the Coast
Range sculpin (Cottus aleuticus) and Pacific lamprey (Lampetra
tridentate), all native species observed in coastal streams
were observed in San Francisquito Creek, which also supports populations
of riffle sculpin (Cottus gulosus), California roach (Hesperoleucaus
symmetricus), and hitch (Lavinia exilicauda) (SUNRI
1999). Historic records indicate that Sacramento perch (Archpoplits
interruptus) and speckled dace (Rhinichthys osculus)
may also have occurred there. However, there are more introduced
species than native species in bayside streams like San Francisquito
Creek, with a list that includes brown bullhead catfish, black
bullhead catfish, mosquitofish, green sunfish, bluegill, pumpkinseed,
redear sunfish, rainwater killifish, largemouth bass, black crappie,
and goldfish (SUNRI 1999). In coastal streams in Santa Cruz County,
there are many native species including speckled dace, Sacramento
sucker (Catostomus occidentalis), sculpin (Cottus
sp.), and roach (Lavinia sp.) (K. Schroeder, pers.
comm. 2004).
References
Conrad, M.T., S. Chartrand, and J. Owens. 2003. "Gazos
Creek Watershed Assessment and Enhancement Plan." Coastal
Watershed Council and Balance Hydrologics. Prepared for California
Coastal Conservancy and California Department of Fish and Game,
92 (plus appendices) pp. View
on-line source.
Stanford University Natural Resources Inventory (SUNRI). 1999.
Fishes of Stanford University [Web site]. Planning Office / University
Architect, Facilities Operations, and Center for Conservation
Biology [cited July 23, 2003]. View
on-line source.
Federal Interagency Stream Restoration Working Group (FISWRG).
1998. "Stream Corridor Restoration: Principles, Processes,
and Practices." GPO Item No. 0120-A; SuDocs No. A 57.6/2:EN3/PT.653. View
on-line document.
Hall, E.R. 1981. The Mammals of North America. Second Edition
ed. New York: John Wiley & Sons.
Raedeke, K.J., R.D. Taber, and D.K. Paige. 1988. Ecology of
Large Mammals in Riparian Systems of Pacific Northwest Forests.
In Streamside Management: Riparian Wildlife
and Forestry Interactions,
edited by K. J. Raedeke. Seattle, WA: University of Washington,
Institute of Forest Resources.
Riparian Habitat Joint Venture (RHJV). 2000. "Version 1.0.
The Riparian Bird Conservation Plan: A Strategy for Reversing
the Decline of Riparian Associated Birds in California." California
Partners in Flight. View
on-line document.
Swanson Hydrology and Geomorphology, Native Vegetation Network,
and Hagar Environmental Science. 2002. "Lower San Lorenzo
River and Lagoon Management Plan." Prepared for City of
Santa Cruz Redevelopment Agency, San Lorenzo Urban River Task
Force, City of Santa Cruz, State Coastal Conservancy.
Warner, R.E. 1979. "The California Riparian Study Program.
Phase I: Background Studies and Program Design for Phase II." California
Department of Fish and Game, Planning Branch. 179 pp.
Williams, D.F., and K.S. Kilburn. 1984. Sensitive, Threatened,
and Endangered Mammals of Riparian and other Wetland Communities
in California. In California Riparian Systems:
Ecology, Conservation, and Productive Management, edited by R. E. Warner and K. M. Hendrix.
Berkeley, CA: Berkeley: University of California Press. View
on-line source.
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