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Niño year. For example, in Chile and Peru, thousands of
seabirds died during the 1982-1983 El Niño, and the valued
ecosystem of Ecuador's Galapagos Islands was disrupted (Ribic et
al., 1992; Trillmich and Limberger, 1985). In California, the
warmer coastal waters of El Niño years reduce the fish
populations that support seals and other marine mammals, resulting
in die-off and reproductive failures (Shane, 1994). Coral reefs are
also vulnerable. They experience bleaching under warm water stress
and can have high mortality rates in El Niño years (Glynn,
1984). Some species, however, such as shrimp and scallops, flourish
in the warmer waters of these years. Managing fluctuations in
marine mammal and bird populations is difficult, especially when
conservation might involve cutting back on commercial fisheries.
Groups have attempted to rescue a few mammals and provide emergency
food supplies to birds.
Many riparian and grassland ecosystems are also highly sensitive
to climatic variability. Coping systems affecting livestock
production on grassland ecosystems are discussed in an earlier
section. However, there is significant climate-related variability
in the populations of less-managed species in riparian and
grassland systems, including breeding birds and amphibians in
marshes and wetlands and grassland wildlife populations ranging
from rodents to grazers to large carnivores. Severe droughts in
southern Africa, for example, are often associated with large-scale
mortality of wildlife.
Water Supply and Flood Management
Climate-driven variability in supply is a fundamental
characteristic of surface water resources. Various water management
entities around the world have planned their infrastructure and
operating procedures in response to expected variations in
hydrologic conditions. In the United States, these entities range
from individual irrigators and domestic water users who control
their own water supply systems to federal agencies that oversee the
operation of complex multiunit, multiple-purpose water storage,
control, and delivery systems. Institutional contexts, which differ
markedly between the arid western and humid eastern states, shape
the efforts of water users and the large variety of public water
managers to cope with variable streamflows. Similarly, other
countries have developed institutions and infrastructure for water
control and allocation that are the product of particular physical,
climatic, and social circumstances. Such arrangements include
small-scale traditional irrigation systems that are often managed
according to complex allocation rules designed specifically to cope
with the effects of variable water supplies, as well as large-scale
modern irrigation projects, typically managed by agents of the
central government.