Estuarine and Lagoon Conditions
Importance to Salmonids
Estuaries and lagoons are critical to adult and juvenile coho
salmon (Oncorhynchus kisutch) and steelhead trout (O.
mykiss).
Young salmonids use estuaries as nursery habitat and as a physiological
transition zone in which to prepare for life in the marine environment.
Lagoons and estuaries are important as rearing habitat, especially
in small coastal streams such as those in San Mateo and Santa
Cruz Counties, where freshwater rearing habitat is often limited.
Smith (1990) suggests that lagoon areas may produce the majority
of smolts from these small coastal stream systems. Because of
intense predation pressure and the need for large amounts of
food resources prior to out-migration, estuarine conditions are
ideal when characterized by high levels of habitat complexity
and abundance of macroinvertebrates. Adults use estuaries as
a place to rest and feed prior to starting their upstream migration.
Upstream migration of adults is often triggered by high outflow
in combination with high tides.
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A lagoon and sand bar have formed near the mouth of
Scott Creek – a coho and steelhead bearing
stream in Santa Cruz County.
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Estuaries and lagoons in San Mateo and Santa Cruz Counties tend to be small, with large fluctuations in freshwater levels and the formation of a sandbar during summer and fall low flow periods. In general, fish diversity increases with lagoon size in this area, and salmonid viability in these lagoons is dependent upon a complex interaction of physical and biotic features and processes, including temperature, salinity, dissolved oxygen, hydro-geomorphology, large wood, phytoplankton, aquatic vegetation, invertebrates, and so forth.
Human Impacts
Human impacts to lagoons and estuaries vary widely, depending
upon the watershed that the estuary drains, as well as localized
land uses. Some estuaries are downstream of relatively undeveloped
watersheds, whereas others are situated at the mouth of river
systems characterized by substantial upslope disturbance from
agriculture, logging, and urbanization. These land uses may result
in excessive levels of sediment, loss of large wood, modification
of freshwater inflows, or the influx of pollutants. In addition
to watershed land use impacts, local lagoon-specific impacts
such as artificial sandbar breaching can cause imbalances in
fresh and saline ratios, and allow predators into the estuarine
area. Other direct impacts to estuaries and lagoons in the area
include diversion for agricultural and municipal uses and diking
of surrounding wetland areas. There are three harbors within
the study area – the Santa Cruz, Moss Landing, and Pillar
Point Harbors – that also impact lagoons and estuaries
by altering sand deposition patterns and near-shore ocean currents,
and increasing pollutants. These permanent structures require
deep-water access, regular dredging, and the construction of support
structures such as jetties and seawalls that interfere with the
natural ebb and flow of estuary and beach boundaries (Brazil
1998; CCS 2004). Boat maintenance, repair, and refinishing in
harbors contribute oils, lubricants, cleaning solutions, paints,
and dust to the waters (CDFG 2003). Finally, bridges,
such as the Highway 1 bridge over Scott Creek, may influence bar
breaching, potentially delaying upstream migration in the winter,
and causing premature sandbar closure in the spring.
References
Brazil, E. 1998. Slowly but surely, erosion eats away at California's
beachfront property. San Francisco Examiner. View
on-line source.
California Department of Fish and Game (CDFG). 2003. "Market
Squid Fishery Management Plan." View
on-line source.
Center for Coastal Studies (CCS). 2004. Coastal Erosion [Web
site]. Scripps Institution of Oceanography [cited 2003]. View
on-line source.
Smith, J.J. 1990. "The Effects of Sandbar Formation and
Inflows on Aquatic Habitat and Fish Utilization in Pescadero,
San Gregorio, Waddell and Pompinio Creek Estuary/Lagoon Systems,
1985-1989." Department of Biological Sciences, San Jose
State University.
Local References
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.
Habitat Restoration Group. 1990. "Soquel Lagoon Management
and Enhancement Plan." Prepared for City of Capitola, Santa
Cruz County, California Coastal Conservancy, California Department
of Fish and Game, 67 (plus appendices) pp.
General References
Nielsen, J.L., P. Goodwin, C.K. Cuffe, and T. Light. 1994. "Russian
River Estuary Study, 1992 - 1993: Hydrologic, Limnilogical, and
Biological Aspects of an Estuary Management Plan." Planning
Department of Sonoma County. 186 (plus appendices) pp.
Goodwin, P., J.L. Nielsen and C.K. Cuffe. 1993. The tidal Inlet
characteristics of a small California Estuary. Hydraulic
Engineering 93:562-567.
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