Management Plan
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Executive Summary

Section 1
CINMS Management Plan

  1. Introduction
  2. Goals & Objectives

Section 2
The Sanctuary Setting

  1. Regional Context
  2. Sanctuary Resources
    1. Environmental
      Conditions
    2. Living Resources
    3. Cultural/ Historic Resources
  3. Sanctuary Uses
  4. Existing Jurisdictions
    and Management

Section 3
Action Plan

Section 4
Administration

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Channel Islands National Marine Sanctuary
Management Plan

Section 2/The Sanctuary Setting

2. SANCTUARY RESOURCES

The Channel Islands National Marine Sanctuary is located at the transition between two distinct biogeographic coastal provinces: the Oregonian and the Californian provinces (Briggs, 1974). South of Point Conception the cold temperate waters of the California current flowing from the north meet the warm temperate waters of the California countercurrent and seasonally with the Davidson Current, both flowing from the south. The current patterns affect the distribution of marine fauna. Species representative of both cold-temperate and warm-temperate regions thrive in the transition zone, and overlap in their distributions at some locations within the sanctuary. The environmental conditions and resources contributing to the ecological significance of the Channel Islands Marine Sanctuary are described further below.

(a) Environmental Conditions

The sanctuary belongs to a region referred to by geologists as the Southern California Continental Borderland. A glance at bathymetric and geological maps confirms that the Borderland is a complex of basins, canyons, ridges, and shelves skirting high-cliffed islands. The area is also characterized by active seismic faults, shallow oil and gas reservoirs, and natural oil and gas seeps. These are most common in the northern Santa Barbara Channel and are periodic or unconfirmed elsewhere (California State Water Resources Control Board, 1979a, 1979b, 1981a; BLM, 1981c).

The submarine geology of the sanctuary consists of undifferentiated sedimentary rock and quaternary volcanic rock overlayed with unconsolidated sediments including gravel, sand, shell rubble, silt, and clay. The rocky shelves around San Miguel and Santa Rosa Islands are among the widest in California and are evidence of intense oceanographic dynamics that have precluded the accumulation of fine sediments (Welday and Williams, 1975). The abrupt depth change from these shallow shelves to deep trenches combined with the gradation from deepwater silt and clay deposits to shallow sand and rock account for the wide variety of intertidal and subtidal habitats in the sanctuary.

Oceanographic conditions are another influence on the distribution and diversity of sanctuary habitats and resources. When the cold California Current reaches Point Conception, the direction of flow carries it away from the shoreline, inducing a large gyre effect or eddy in the southern California bight. The return flow of this gyre, the southern California countercurrent, moves waters from southeast to northwest, through the Channel Islands toward the mainland. The resulting gyres and eddies affect the distribution of marine fauna leading to the presence of both cold and warm temperate species. Surface and bottom currents also circulate nutrients and pollutants in the sanctuary. For example, currents and winds are known to affect turbidity around the islands, with turbidity generally higher on the north or windward side and to the east off Anacapa and Santa Cruz Islands (California State Water Resources Control Board, 1979a).

An upwelling period occurs in the southern California bight from February or March through August, during which nutrient-rich deep waters are drawn to the surface by offshore winds. During the spring, high nutrient levels combined with increasing day length and light intensity foster exceptionally high phytoplankton and algal productivity. This increase in the food supply supports even greater numbers of fish, shellfish, and other marine life in the sanctuary.

Other aspects of water quality in the sanctuary have been documented only to a limited extent (NPS, 1982b; California State Water Resources Control Board, 1979a, 1979b, 1981a, 1981b; BLM, 1981c). Owing to the absence of municipal or industrial point sources, and relative isolation from mainland sources, water quality around the islands is generally good. However, chronic oil and tar pollution from non-point sources outside the sanctuary is reported as an important concern particularly along the north shore of the islands (California State Water Resources Control Board, 1979a, 1979b). Data collected for the California Mussel Watch Program at stations along the mainland and at the offshore islands indicate significant accumulations of heavy metals at Anacapa, Santa Barbara, San Miguel Island Areas of Special Biological significance (California State Mussel Watch, 1979 in BLM, 1981c). It is not currently known if these levels of pollutants are accumulating at higher trophic levels and whether they are affecting individuals or populations.

Weather conditions in the area tend to be localized and seasonally variable, but typical of a coastal mediterranean climate. Over the course of an average year, January to March are the months receiving the most rain. Associated with the frequent weather fronts are strong winds, poor water visibility, and four to six foot (one to two meter) swells. Winter water temperatures around the Channel Islands do not exceed 55É F to 60É F (13É C to 15É C). Coastal fog and low clouds prevail during April and May and the sea surface grows favorable and predictable weather conditions for diving and boating are from June to October when weather fronts are infrequent and seas are generally calm. Summer fogs are also common. Average water visibilities around the islands are reported between 30 to 40 feet (9 to 12 meters) and water temperatures range from 65É F to 70É F (18É C to 21É C). Stormy and windy conditions tend to prevail again from October to December (Fagan and Pomeroy, 1980).

This yearly weather pattern is considered predictable and is largely responsible for the May to October peak recreational use season. Conditions do vary among parts of the sanctuary. San Miguel Island, for example, is completely surrounded by the cold water mass of the California current and is exposed to the open seas of the Pacific. Nearshore waters are usually colder, more turbid, and subject to heavy surge. Weather conditions are reported to change quickly even during the summer, thus presenting constraints for on-site operations. The Santa Barbara Island nearshore is also exposed to strong westerly winds, but waters are more characteristic of the clear and warm conditions of the California countercurrent. Similar warm and clear conditions prevail in the vicinity of Anacapa Island with nearshore waters being more sheltered by the islands to the west. Conditions around Santa Rosa and Santa Cruz Islands resemble those described for San Miguel Island with the waters around Santa Cruz being somewhat more protected and warmer than those around Santa Rosa Island. The general weather conditions are an important consideration for on-site operations such as surveillance, search and rescue, and oil spill containment in the sanctuary. Differences in the sanctuary suggest distinct safety and Ñcomfortæ zones which can affect the planning of visitor use and interpretation.

 


 

 



Revised by The CINMS webmaster
National Ocean Service | National Oceanic and Atmospheric Administration | U.S. Department of Commerce
http://www.cinms.nos.noaa.gov
channelislands.noaa.gov /marineres/mpsec2.2.html