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Williams and Dodd <br />In 1968, the California Department of Fish and Game coordinated efforts of private or- <br />ganizations, the Los Angeles Water Department (Los Angeles requires part of the water <br />supply from the Owens Valley), and Federal agencies in the establishment of the Owens <br />Valley Native Fish Sanctuary in Fish Slough. After renovation of portions of the wetland <br />to a safe and stable condition, native fishes were reintroduced (Miller and Pfister, 1971). <br />This type of cooperative action is essential if many endangered wetland-dependent species <br />are to survive. <br />Scarcity of water throughout the grid Southwest has focused attention on wetlands as <br />sources of water to fulfill human needs, usually for irrigation or for livestock. Abuse of <br />wetlands has created problems for resident herpetofauna. For instance, marshes are <br />ditched and channelized, thus exposing tadpoles to predation. Cattle trample both toads <br />and tadpoles. As a result, species such as the black toad, Bufo exsul, and Amargosa toad, <br />B. boreas nelsoni, both restricted to very small marshlands in California and Nevada, re- <br />spectively, face an uncertain future (Busack and Bury, 1975). <br />EXAMPLE OF THE WHOOPING CRANE <br />One of the best known endangered birds and perhaps the best example of an endan- <br />gered species' dependence on a variety of wetland habitats is the whooping crane, Gros <br />arnericana. The population at Aransas National Wildlife Refuge reached aloes 13 adults <br />and 2 young - in 1941. Current estimate of remaining wild cranes in the Canadian flock <br />is approximately 75 birds. Prior to human interference, the whooping crane population <br />was estimated at 1,300 to 1,400 birds. Its endangered status and biology have been docu- <br />mented by Allen (1952, 1957). The whooping crane's life cycle encompasses a distance <br />of approximately 4,200 km between the Northwest Territories of Canada and the Aransas <br />National Wildlife Refuge on the Texas coast. In April, whoopers leave the Aransas <br />Refuge, migrating northward along the Central Flyway, arriving at their traditional. breed- <br />ing grounds in Wood Buffalo National Park in the Northwest Territories by late April or <br />early May. Cranes build their nests in wetland areas in water 0.3 to 0.6 m deep and re- <br />main in the area during spring and summer months. The last known whooping crane <br />nest in the United States was observed in 1889 (Miller, et al., 1974). <br />In October, adult and young whooping cranes begin the migratory flight to the Texas <br />Gulf coast passing through southern Canada, northeast Montana, North Dakota, South <br />Dakota, Nebraska, Kansas, Oklahoma, and Texas. Along the path, riverine wetlands are <br />essential for feeding and resting. Cranes feed on aquatic plants and animals in marshes <br />and use wet meadow areas and islands along braided river channels as roosting areas. <br />Along the migratory route, most of the crane's critical habitat areas, identified by the LJ.S. <br />Fish and Wildlife Service, are wetlands located along stream bottoms and reservoirs <br />(Sheppard, 1978a, 1978b). <br />Whooping cranes spend the winter in tidal marshes along the Texas coast. Upon arrival, <br />pairs and families of cranes establish feeding and roosting territories. Salt and fresh water <br />marshes provide for the crane,~t„an abundance of food organisms -blue and fiddler crabs, <br />clams, shrimp, and crayfish. <br />Decline of the whooping crane population resulted from illegal shooting and destruction <br />of wetlands. Wildlife laws enacted during the early 1900's virtually eliminated illegal <br />shooting, but unfortunately did nothing to prevent continuing destruction of the cranes' <br />wetland habitat. <br />572 <br />