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Population Dynamics of Breeding Waterfowl

V. Egg Survival

A. Nest Success


Nest success (the probability that a clutch will survive to produce at least one hatchling) is one of the most studied aspects of waterfowl biology. Many studies, unfortunately, either cannot or do not distinguish among the various causes of nest losses. Also, interpretations of nest losses are suspect, because more than one agent of destruction may operate on a single nest; for example, a nest may be abandoned because a predator visited it, or an abandoned nest may later be depredated. Further, more than one species of predator may consume eggs within a single clutch, and only the latest or most conspicuous is accused.

Another confounding problem is that, until recently, most nesting studies did not recognize the bias of nest success estimates based on samples of nests that have already survived various periods of time before being found. Mayfield (1961) proposed an analytic technique to overcome some such problems, but his method was little-used until recently (Miller and Johnson 1978).

Losses of entire clutches have been attributed to predation, abandonment, agriculture, weather, and human disturbance. These may operate in concert. Because causes of loss are often not reliably known, some reports discuss nest success in general, others describe losses attributable to specific causes.

1. Age, Breeding Experience, and Condition of the Bird

Greater nest success among older birds was reported for Wood Ducks (Hansen 1971) and Lesser Scaup (Afton 1984) but not for Mallards (Cowardin, Gilmer, and Shaiffer 1985). Ewaschuk and Boag (1972) and Patterson and Makepeace (1979) found higher nest success among socially dominant individuals for Canada Goose and Northern Shelduck, respectively.

Abandonment may be more likely among young or less experienced females (Alliston 1979a, Heusmann 1984) or those in poor physical condition. Braithwaite (1982) indicated that a failure in food supplies may be the major cause of abandonment by Black Swans.

2. Nesting Habitat

Numerous investigators have noticed variation in nest success rates among habitats. These differences may relate to differing abundances of predators (Johnson, Sargeant, and Greenwood 1989), concealment from predators (Hines and Mitchell 1983b, Hill 1984b), susceptibility to severe weather (Ely and Raveling 1984), vulnerability to agricultural destruction (Cowardin, Gilmer, and Shaiffer 1985), or exposure to human vandalism (Haramis 1975). Prop, van Eerder, and Drent (1984) reported higher nest success of Barnacle Geese in areas with near good feeding sites, which reduced the absences of the gander.

Although nest losses to predation should obviously vary with predator numbers, few studies (e.g., Johnson, Sargeant and Greenwood 1989) have documented this, usually because of the difficulty of indexing predator numbers. Study areas from which predators have been excluded, however, consistently show high nest success (Balser, Dill, and Nelson 1968; Duebbert and Kantrud 1974; Duebbert and Lokemoen 1980; Lokemoen et al. 1982).

Some sites offer protection from predators. Predation is often lower on islands than on mainland (Mihelsons 1968; Schamel 1977; Giroux 1981a, b; Duebbert, Lokemoen, and Sharp 1983), especially islands farther from shore (Giroux 1981a) or farther from gull colonies (Odin 1957). Predation may be lower on nests well-concealed by vegetation (Odin 1957, Hill 1984b, Sugden and Beyersbergen 1987), but not all investigators (e.g., Kalmbach 1937, Hammond 1940, Keith 1961) found the anticipated effect. Johnson, Sargeant, and Greenwood (1989) found predation rates on duck nests to vary according to precipitation patterns and wetland conditions, which they suggested might relate to improved vegetation around the nest or increased numbers of buffer prey. Afton (1984) and Cowardin, Gilmer, and Shaiffer (1985) detected higher nest success of Lesser Scaup and Mallards, respectively, in years or areas with many wetlands. In an experiment, Bowman and Harris (1980) found reduced foraging efficiency by raccoons with increased spatial heterogeneity of nesting habitat.

Buffer prey, usually small mammals, can reduce depredation on upland nests (Hanson and Smith 1950, Barry 1967, Byers 1974, Eisenhauer and Kirkpatrick 1977, Weller 1979, Summers 1986). Crabtree and Wolfe (1988) reduced predation on waterfowl nests by experimentally providing alternative foods for striped skunks. Conversely, Ryder (1961) found little evidence that American Coot clutches buffered losses of duck nests in marshes. An indirect buffering was proposed by Bousfield and Syroechkovskiy (1985), who observed that in years of low lemming populations, fewer arctic foxes had litters, so they ranged more widely and inflicted damage to more Snow Goose nests.

Waterfowl sometimes nest among larids or other, usually colonial, birds. Blomqvist and Elander (1988) showed that King Eider nests were significantly clustered near those of Long-tailed Skuas. Arctic Terns, Black Turnstones, or larids may provide protection against avian predators for ducks and geese nesting among them (Barry 1967, Mihelsons 1968, Evans 1970, Mickelson 1973, Kistchinski and Flint 1974, Schamel 1977, Young and Titman 1986, Götmark and Åhlund 1988), although some larids themselves will depredate eggs or ducklings (Dwernychuk and Boag 1972). Canada Geese may offer some protection for ducks (Giroux 1981b) or Graylag Geese (Fabricius et al. 1974). A similar interspecific phenomenon involved an Eider colony growing rapidly under protection afforded by tethered husky sledge dogs (Meltofte 1978).

The land use of a nesting habitat can affect nest success. Waterfowl nests constructed in hayland are vulnerable to mowing losses (Labisky 1957, Evans and Wolfe 1967, Mihelsons 1968, Livezey 1981) or predation because of increased exposure (Labisky 1957, Mihelsons 1968). Nests in areas subjected to grazing may be trampled (Moyle 1964, Gjersing 1975), and those in cropland sometimes suffer plowing or other agricultural destruction (Meanley and Meanley 1959, Higgins 1977). In addition, nests are destroyed by fires set by farmers (Stoudt 1971, Fritzell 1975) or grassland managers (Kruse and Piehl 1986).

3. Density and Parasitism

Evidence of an effect of nest density on predation loss is conflicting. Positive correlations between nest density and nest success rate (e.g., Gorman 1974) typically do not account for the greater likelihood of finding nests where the success rate is high. Dense concentrations of nesting birds may provide protection against certain predators (McLandress 1983; Schmutz, Robertson, and Cooke 1983; Bousfield and Syroechkovskiy 1985). Conversely, a decrease in nest success with greater nest numbers was reported by Marshall (1967), Weller (1979), and Hill (1984a).

Abandonment rates can be high in dense nesting situations (Newton and Campbell 1975; Duebbert, Lokemoen, and Sharp 1983) or when parasitism is substantial (Dement'ev et al. 1967, Brown and Brown 1981, Giroux 1981c, Eriksson and Andersson 1982). Primary causes of nest abandonment in dense nesting situations include competition for nest sites and interference from other birds (Grenquist 1963, Anderson 1965, Titman and Lowther 1975). Ewaschuk and Boag (1972) considered attacks by neighboring males to cause abandonment of Canada Goose nests. Duebbert, Lokemoen, and Sharp (1983) attributed high abandonment rates of Mallards and Gadwalls on a crowded island to harassment of nesting females by males, rather than to inter- or intraspecific parasitism. Gauthier and Smith (1987) suggested that in one year desertion by Buffleheads was density-dependent among first-time nest box users.

4. Humans and Weather

Humans can act as predators on waterfowl clutches. Although egg collection for food or hobby is far less prevalent now than historically (Gross 1944, Mihelsons 1968, Bousfield and Syroechkovskiy 1985), it remains a serious factor in some populations (Eisenhauer and Kirkpatrick 1977). Disturbances, usually human-caused, can lead to depredation of clutches (Joensen 1973, Milne and Reed 1974, Livezey 1980, Reed 1975), exposure to adverse weather, or abandonment (Anderson 1965; Balát 1969; Culbertson, Cadwell, and Buss 1971). Visits to nests in the egg-laying stage are more likely than later visits to induce abandonment (Sowls 1951).

Weather phenomena leading to abandonment include snowstorms (Heusmann 1984), heavy rains (Dement'ev et al. 1967, Heusmann 1984), and late ice breakup (Fredga and Dow 1984). For nests in low-lying situations, flooding can be an important cause of abandonment (Andrews 1952, Hildén 1964, Joyner 1977, Livezey 1980).

5. Other Factors

Many researchers have noticed differences in nest success among species, possibly due to variation in nesting phenology (Vermeer 1968), nesting habitat, ability to repel predators, or nest attentiveness (Eisenhauer and Kirkpatrick 1977). Also, proclivity to abandon may vary among species (Siegfried 1965). Nest success has been found to be higher in years with early springs in far-north areas (Didiuk and Rusch 1979; Prop, van Eerden, and Drent 1984). Among Snow Geese, the presence of the male significantly increased nest success (Martin et al. 1985). Swennen (1983) found low nest success of Eiders during years when food supplies were contaminated with chlorinated hydrocarbons. Blus et al. (1979) noted lower nest success, probably caused by desertion, of Canada Geese from clutches with high residues of heptachlor and other contaminants. The authors were unsure if desertion preceded or followed embryonic death.

Visits to nests by predators can lead to abandonment (Bellrose, Johnson, and Meyers 1964; Cowardin, Gilmer, and Shaiffer 1985; Haramis and Thompson 1985; Greenwood et al. in prep.), as can trampling by cattle (Thomas 1980). Partially depredated nests may be more likely to be abandoned (Haramis and Thompson 1985). The death of a hen away from the nest will cause the appearance of nest abandonment (Livezey 1980).


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