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.
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