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Justification Justification of Red List Category This species has an extremely large range, and hence does not approach the thresholds for Vulnerable under the range size criterion (Extent of Occurrence 30% decline over ten years or three generations). The population size is very large, and hence does not approach the thresholds for Vulnerable under the population size criterion (10% in ten years or three generations, or with a specified population structure). For these reasons the species is evaluated as Least Concern. Trend justification The overall trend is decreasing, although some populations may be stable (Wetlands International 2006). Spi serial flash programmer schematic drawings. Ecology Behaviour This species is largely sedentary over much of its range (del Hoyo et al.

1992), although it may make seasonal nomadic or dispersive movements related to water availability (Brown et al. 1982, del Hoyo et al.

1992, Kear 2005a). It also undertakes annual post-breeding moult migrations to favoured waters (Kear 2005a). The timing of the breeding season in this solitary nester varies geographically, with pairs in some regions nesting in the spring or at the end of the dry season (del Hoyo et al.

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1992), whereas nesting in other areas, such as southern Africa, peaks in the middle of winter and does not necessarily correspond with local rainfall patterns (G. Cumming in litt. Outside of the breeding season the species may occur in flocks consisting of hundreds or thousands of individuals (e.g. During moult), although it is most common in pairs or small groups (Kear 2005a). It forages diurnally (Kear 2005a), mostly in the morning and evening (Johnsgard 1978). Habitat The species inhabits a wide range of freshwater wetlands in open country from sea level up to 4,000 m (Ethiopia) (Madge and Burn 1988, del Hoyo et al. 1992), including reservoirs, dams, pans, lakes, large ponds, rivers, marshes, sewage works, estuaries and offshore islands (Kear 2005a) (although it is generally absent from coastal regions) (Brown et al.