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

(b) Living Resources

The area was selected and designated as a national marine sanctuary because of concentrations of these living resources of exceptional significance: (1) marine mammals (pinnipeds and cetaceans); (2) seabirds; (3) fish, shellfish, and kelp; and (4) intertidal organisms (Department of Commerce, 1980). A review of these resources is helpful in understanding the populations and ecological linkages being protected, their status, and options for protection.

Pinnipeds

The dramatic recovery of pinniped populations in the Channel Islands since the end of the fur trade has been documented through several systematic studies in recent decades (Le Boeuf and Bonnell, 1980). Past and on-going research has also helped establish the status of seals and sea lions in different parts of the Southern California bight including the Channel Islands National Marine Sanctuary.

The Channel Islands National Marine Sanctuary currently provides habitat for breeding populations of five species of pinnipeds; the California sea lion, the Stellar sea lion, the northern fur seal, the northern elephant seal, and the harbor seal. A sixth species, the Guadalupe fur seal, is an occasional visitor to the area. All six species are found in the sanctuary at different times of the year, feeding on the abundant fish and invertebrate resources of the island shelves or hauling out on rocks and beaches.

Pinniped speciesÖ diversity and concentration varies across the sanctuary. The greatest numbers occur around the western tip of San Miguel Island, the only location in the United States, and one of the very few in the world, where breeding populations of five species of pinnipeds can be found. Three species“California sea lions, northern elephant seals, and harbor seals“breed at Santa Barbara Island. Harbor seals breed on Santa Rosa, Santa Cruz, and Anacapa Islands. The life history of each species has been described elsewhere (see Department of Commerce, 1980). The description below focuses on aspects relevant to the sanctuary resource protection program.

The California sea lion (Zalophus californianus) is the most abundant and widely distributed pinniped of the sanctuary with approximately 30,000 individuals hauling out and breeding in the area (NMFS, 1982). These numbers represent about 25 percent of the total world population. San Miguel Island is also considered the northernmost rookery for this species. Estimates for 1981 set the annual pup production in the sanctuary at 8,955 with San Miguel accounting for most of these numbers (NMFS, 1982). Some pups are also born at Santa Barbara Island. Growth of the San Miguel population in the last two decades has been rapid and is expected to continue (Le Boeuf and Bonnell, 1980).

Premature pupping and aborted pups have been reported in recent years but it is currently not known whether human-related factors such as pollution or natural causes are involved (Le Boeuf and Bonnell, 1980). The northern elephant seal (Mirounga angustirostris) is the largest and second most abundant pinniped in the sanctuary. The total population in 1981 was estimated at 24,000 or 38 percent of the worldÖs total population (NMFS, 1982). Elephant seal rookeries are located on Santa Barbara and San Miguel Islands“the latter now being the largest colony in the world (De master, pers. comm.) Total pup production in 1981 was estimated to be 7,125 and further rapid growth of the San Miguel Island population is expected (NMFS, 1982). Le Boeuf and Bonnell (1980) report that elephant seal groups have expanded their breeding area on the island from 1968 to 1979 to include virtually the entire southern shore. Colonies may be forming on the northern shore and establishment on the islands further to the east is also a possibility.

The small colony of northern fur seals (Callorhinus ursinus) on San Miguel Island represents the southern breeding limit for this species. It is also the only colony along the eastern Pacific south of Alaska. Since about 100 individuals were first discovered at Adams Cove in 1968, the population has grown exponentially to about 2,195 animals in 1981 of which 1,220 were pups (NMFS, 1982). The species has also expanded its breeding area to include Castle Rock. The waters within 3 miles (5 km) of both rookeries are reported areas of concentration (BLM, 1981c).

All five islands (San Miguel, Santa Rosa, Santa Cruz, Anacapa, and Santa Barbara) are hauling sites and rookeries for harbor seals (Phoca vitulina). The total population in 1981 amounted to about 2,100 individuals, with the largest colonies occurring on Santa Rosa and San Miguel Islands (NMFS, 1982). Le Boeuf and Bonnell (1980) report that the harbor seal population has been increasing slowly but consistently in southern California and throughout their range. This species is much more wary than any of the other pinnipeds found in the Channel Islands area, avoiding pupping at beaches used by other species and also avoiding areas that are chronically disturbed by human activities (NMFS, 1982).

Since 1968, the Stellar or northern sea lion (Eumetopias jubatus) has been observed in the southern California bight only on San Miguel Island (Point Bennett, Richardson Rock, Castle Rock), and in steadily decreasing numbers (Le Boeuf and Bonnell, 1980). The island is also the speciesÖ southernmost rookery. Total numbers breeding on San Miguel Island are thought to be low, with the total state population estimated at 1,000, and with no more than 5 pups being born annually (NMFS, 1982). Factors contributing to the decline of the population are not understood, but may involve a decline in prey availability, competition with other pinnipeds, fluctuations in habitat parameters, or some combination of these factors (NMFS, 1982).

The Guadalupe fur seal (Arctocephalus townsendi) currently breeds only on the Isla de Guadalupe in Mexico although it was once a resident of the Channel Islands. In recent years, occasional male Guadalupe fur seals have been sighted on San Miguel Island but pups have not been observed to date (NMFS, 1982). This species is listed by the State of California as rare. It is also being considered for listing under the Federal Endangered Species Act (R. Hofman, pers. comm.).

In summary, the significance of the pinniped resources of the sanctuary rests on the following characteristics:

  • It is one of the few areas of the world with an overlap in distribution of species characteristic of warm-temperate waters (i.e., the California sea lion, the Guadalupe fur seal) and cold temperate waters (northern fur seal, Stellar sea lion);
  • The rookeries for several species have been expanding in recent years and further growth is expected;
  • For some species, the sanctuary population represents a high percentage of either the southern California population or the worldÖs total population;
  • The indication that sanctuary waters must be highly productive to support such a large and rapidly growing mammal population; and
  • The populations are relatively accessible to major urban centers, providing opportunities for research and interpretation.

While much is now known about the status of pinnipeds, several key questions remain with respect to their ecology and behavior that may affect how they can be protected in the sanctuary. Management concerns which are being jointly addressed by agencies such as the National Marine Fisheries Service, the CF&G, and the Sanctuary Programs Division include: (1) the nature and extent of interactions between pinnipeds and several net fisheries; (2) the effects of hydrocarbon spills and chronic pollution on individuals and populations; (3) the potential effects of the Space Shuttle Program; (4) food requirements of pinniped populations and their implications for fisheries management; and (5) the need to minimize existing and future levels of human disturbance.

Cetaceans

At least 27 species of whales and dolphins have been sighted in the sanctuary. About 18 species are seen regularly and of these common dolphin, Pacific white-sided dolphin, bottlenose dolphin, DallÖs porpoise, northern right whale dolphin, short-finned pilot whale, killer whale, and minke whale are considered Ñresidentsæ (Leatherwood, pers. comm.). RissoÖs dolphin, fin whale, humpback whale and gray whale are other species possibly residing in the sanctuary. Very little is known concerning the areas of concentration, life history, or behavior of the resident populations in the sanctuary.

The sanctuary also lies on the migratory pathway of the California gray whale and other large baleen and toothed whales. Gray whales with calves have been observed in the nearshore kelp beds of the sanctuary which are thought to offer protection from strong seas and resting habitat for calves (Leatherwood, pers. comm.). The Pacific right whale, one of the rarest of the great whales, has also been sighted in the area.

Cetaceans are considered a significant sanctuary resource because of the frequency and diversity of sightings in the vicinity of the islands, and the fact that the worldÖs total populations are so small.

Marine Birds

Marine birds constitute another significant resource because of the large concentrations and high species diversity observed in the sanctuary. Over 60 species may be using sanctuary waters to varying degrees as nesting and feeding habitat, for wintering, and/or as migratory staging areas (Department of Commerce, 1980).

Of the sixteen resident species of marine birds in the southern California bight, eleven breed in the sanctuary. Some of the colonies represent large percentages of the southern California or statewide total population (Sowls et al., 1980).

San Miguel Island, together with its small islets (i.e., Prince Island, Castle Rock, and Richardson Rock) supports the most abundant and diverse avifauna in the sanctuary. Nine species have established colonies on the island and form dense feeding concentrations in nearshore waters during their nesting season. Santa Barbara Island has several nationally and internationally significant seabird colonies including the largest XantusÖ murrelet colony in the United States and the only U.S. colony of black stormpetrels.

The only permanent rookery in California for the brown pelican“an endangered species“occurs on Anacapa Island. As with the other marine birds, this species is critically dependent of the abundant fish resources of the sanctuary. The island also supports a large western gull colony.

In summary, the significance of the marine bird resources of the sanctuary is based on the following characteristics:

  • The large concentrations and high species diversity, particularly in the vicinity of San Miguel, Santa Barbara, and Anacapa Islands;
  • The presence of a unique colony of an endangered species (the brown pelican) and several other rare species on Anacapa and Santa Barbara Islands, all of which depend on the productivity of sanctuary waters; and
  • The colonies and nearshore feeding habitats accommodate major percentages of the StateÖs total populations that no longer breed on the southern California mainland.

The biology and ecology of a few species of marine birds such as the California brown pelican and the western gull have been well documented in the sanctuary (NPS, 1982b; Ingram et. al., 1983). If the distribution of nesting colonies are known for most other species, information is lacking on colony sizes across the sanctuary, reproductive success, foraging areas and habits. A handbook has recently been [prepared to guide monitoring of selected seabird species of the national park and sanctuary (Ingram et. al., 1983). If the distribution of nesting colonies are known for most other species, information is lacking on colony sizes across the sanctuary, reproductive success, foraging areas and habits. A handbook has recently been prepared to guide monitoring of selected seabird species of the national park and sanctuary (Ingram et al., 1983). The monitoring program will be used to detect changes in seabird populations over time.

Other management concerns being addressed by agencies such as the NPS, the U.S. Fish and Wildlife Service, the CF&G, and others include: (1) the food habits and biomass requirements of some species and possible effects on commercial fishery stocks; (2) interactions with certain types of fishing practices; and (3) the effects of hydrocarbon spills and other types of pollution on various species.

Subtidal Invertebrates, Fish, and Kelp

Descriptions of subtidal environments and species assemblages are available, albeit not complete, for some sites within the Channel Islands National Marine Sanctuary (California State Water Resources Control Board, 1979a, 1979b; NPS, 1982b). The predominant nearshore communities are: (1) the kelp forest rock bottom community, and (2) the shallow sand bottom community (CF&G, 1979).

The kelp forest rock bottom community is by far the better studied nearshore habitat type in the sanctuary. Luxuriant forest-like growth of giant kelp (Macrocystis pyrifera) occurs in shallow waters, usually from 26 ft (8 m) to 112 ft (34 m) throughout the sanctuary (CF&G, 1979; Department of Commerce, 1980). While the kelp canopy will vary from year to year depending on storms and other factors, the most dense and extensive formations occur along protected island shores (e.g., the southwest side of San Miguel Island, southern and western shores of Santa Rosa, around all of Anacapa Island, the northeast side of Santa Barbara Island). Several other numerous brown algae (e.g., Agarum sp., Laminaria farlowii, Pterygophora californica) occur in association with giant kelp. Other subtidal algal zones reported in the sanctuary are: (1) a shallow zone from the intertidal to 26 ft (8 m) dominated by other brown algae such as southern palm kelp (Eisenia arborea), feather boa kelp (Egregia sp.), and Laminaria farlowii; and (2) a deeper zone below 112 ft (34 m) typified by small red algae (Rhodophyta) and scattered Agarum fimbriatum (California State Water Resources Control Board, 1979a; Neushul, 1967; see also CF&G, 1979 for a more complete list of common algae).

The kelp forest rocky bottom community occurs in association with an unusually diverse and abundant invertebrate fauna (CF&G, 1979). However species lists are available only for a few sites such as the ecological reserves (around Anacapa and San Miguel Islands) and Areas of Special Biological Significance. Additional research is required to delineate areas of exceptional significance. Large conspicuous invertebrates of the rocky bottom kelp forest include several sponges, kelp crabs, spiny lobster, abalone, octopus and squid, sea stars, and sea urchins. Common fish of the kelp forest community include garibaldi, opaleye, kelp bass, California sheepshead, sea perch, painted greenling and several species of rockfish.

Shallow sandy bottoms are another nearshore subtidal habitat prevalent in the sanctuary (CF&G, 1979). Except in very calm shallow coves, sandy substrates do not support extensive algal growth. Fish and invertebrate species tend to be less diverse and abundant than in kelp forest communities. Common species include sea pansies, polychaetes, sand dollars, several species of rays, sanddab, and turbot (CF&G, 1979).

Accurate characterizations of the deeper subtidal habitats of the sanctuary are extremely limited (CF&G, 1979). Surveys have shown that the benthic fauna of the silt-dominated canyons is diverse (CF&G, 1979). The walls of such canyons are often covered by a dense animal Ñturfæ“a thin living mat of encrusting sponges, bryozoans, and tunicates. Equally high diversities and concentrations are found in the offshore pelagic environment of the sanctuary. Common pelagic invertebrates include several copepods and euphausiids, a pelagic shrimp, squid, and the pelagic red crab. Over 30 species of fish are also common to the pelagic environment of the sanctuary. Concentrations of the pelagic schooling species such as northern anchovy are a critical food source for other sanctuary inhabitants, such as the brown pelican.

Intertidal Organisms

Intertidal fish and invertebrates of the Channel Islands have been comparatively well documented (Littler, 1980). Common habitat types include rock shelves, boulder beaches, tidepools, rubble piles, and sand flats. A diverse and abundant fauna is reported at the sites that have been surveyed (California State Water Resources Control Board, 1979a, 1979b, 1981a, 1981b). Common species include acorn barnacles, periwinkles, limpets, chitons, sea stars, shore crabs, several species of brown, red, and green algae, sea lettuce, California mussel, and black and green abalone. Black abalone concentrations in remote areas of Santa Cruz, Santa Rosa and San Miguel Islands are particularly significant as these no longer occur in more accessible areas.

 


 

 



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/mpsec2.2b.html