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Population Dynamics of Breeding Waterfowl

II. Number of Potential Breeding Birds

A. Survival


As a principal determinant of both fitness and population growth, annual survival rate is of interest to both evolutionary biologists and wildlife managers. Annual survival rates can be estimated with data from band recoveries, capture-recapture (including capture-resighting), or radio-telemetry. Although the waterfowl literature is replete with survival estimates based on band recoveries, many such estimates are based on outmoded methods and may be severely biased (Eberhardt 1972, Seber 1972, Anderson and Burnham 1976, Burnham and Anderson 1979). We restrict attention primarily to estimates based on the models described by Brownie et al. (1985), which include those of Seber (1970), Robson and Youngs (1971), and Brownie and Robson (1976).

1. Species

Variation in survival among species is important whether we are interested in the evolution of life history characteristics (Stearns 1976) or species-specific management programs. Although some authors (Patterson 1979, Bailey 1981) have examined interspecific variation in life history strategies of North American duck species, we are not aware of any previous attempt to assemble survival rate estimates based on modern estimation models for a variety of waterfowl species.

Among the North American anatids, geese tend to have higher survival rates than ducks, and the single estimate for swans is highest of all (Table 14-1). Larger species tend to have higher survival rates. Survival and several components of reproductive rate appear to be allometrically scaled to size in mammals (Western 1979, Stearns 1983), and probably birds as well (Lindstedt and Calder 1976, Sæther 1987).

Blandin (1982) and Krementz et al. (1987) calculated lower survival estimates for Black Ducks than the average estimates for Mallards presented by Anderson (1975b). These estimates were not strictly comparable, however, as they represented different geographic areas and time periods. Nichols, Obrecht, and Hines (1987) found no consistent differences in survival rates between the two species for birds banded in the same areas and time periods (also see Heusmann 1981 for a similar comparison).

2. Age

Recent studies have corroborated the belief of waterfowl biologists that young birds have lower annual survival rates than adults. Lower survival rates for young birds than for adults have been found in Canada Geese (Krohn and Bizeau 1980, Pollock 1981, Stotts 1983), Wood Ducks (Nichols and Johnson 1990), Mallards (Anderson 1975b), Black Ducks (Blandin 1982, Krementz et al. 1987), Pintails (Rienecker 1987), Blue-winged Teal (L. D. Schroeder pers. commun.) and Ring-necked Ducks (Conroy and Eberhardt 1983). These studies compared birds banded during summer or early fall as young (hatched the same year) and adults (hatched at least l full year previous to the time of banding).

Bandings in winter of Canada Geese, Mallards, and Canvasbacks have provided insight into when age-specific survival differences occur. Tests for age-specificity of survival rates of winter-banded Canada Geese have yielded diverse results. Most tests (e.g., Trost, Rusch, and Anderson 1981; Stotts 1983) have found no evidence of age-specific survival differences. Kasul and Wright (1980), however, found that survival rates of young banded during winter in southern Illinois were significantly lower than those of adults during two out of three time periods tested. The 1960-77 period, with the largest banded samples, yielded estimates of 0.77 for young geese and 0.82 for adults (Kasul and Wright 1980).

Although winter-banded Mallards showed no evidence of age-specific differences in survival rates (Hopper, Funk, and Anderson 1978; Rakestraw 1981; Nichols and Hines 1987), radiotelemetry mortality studies of female Mallards in the Mississippi Alluvial Valley during late fall and winter did detect age-specific differences in mortality (Reinecke, Shaiffer, and Delnicki 1987). We conclude that by late winter any mortality differences between first-year and older Mallards are small and that large age-specific differences observed for preseason-banded Mallards occur primarily between August and February, including the fall migration and hunting season (also see Nichols and Hines 1987).

Analyses of Canvasbacks banded on Chesapeake Bay during winter also suggested lower survival rates for young birds (G. M. Haramis, pers. commun.). Because the tests were based on capture-recapture data, age-related differences in permanent emigration may have contributed to the difference.

Age-specificity in survival beyond the first year has not been investigated thoroughly in waterfowl. Although age-specific survival rates can be estimated for virtually any number of initial age classes using standard band recovery and capture-recapture models, these models have been little used beyond the two-age (young and adult) case because they require that newly banded birds be assigned to more than two age classes. However, the H2 versus H3 test of Brownie et al. (1985) can detect, but not estimate, differences in survival or recovery rates between second-year and older birds, using data from birds aged to only two age classes. This test occasionally provides evidence of age-specificity beyond two years in data sets for ducks, and somewhat more frequently with Canada Geese, but two-age models fit the data adequately in the large majority of cases (J. D. Nichols, unpubl. data).

Capture-recapture data for known-age cohorts can be used to estimate age-specific survival rates for virtually any number of age classes (Buckland 1982, Parkin and White-Robinson 1985, Loery et al. 1987). Resulting survival estimates are much less robust to heterogeneous survival and capture probabilities than those based on data not separated by cohort (Buckland 1982; Johnson, Burnham, and Nichols 1986; Loery et al. 1987). Nevertheless, cohort analyses can still yield useful estimates and inferences about age-specific survival beyond two age classes (Loery et al. 1987). Parkin and White-Robinson (1985) found for Canada Geese in England an increase in annual survival for the first three to five years and a possible decline in survival probability beyond seven years of age. This analysis is one of the few to provide evidence of senescent decline in survival for any bird species (also see Loery et al. 1987).

3. Sex

The degree of sex-specificity in survival rates seems to depend on both age and subfamily within Anatidae. Among ducks, lower survival rates for adult females than adult males have been reported for Wood Ducks (F. A. Johnson et al. 1986), Mallards (Anderson 1975b, Nichols and Hines 1987), Black Ducks (Blandin 1982, Krementz et al. 1987), Pintails (Rienecker 1987), Canvasbacks (Nichols and Haramis 1980), and Ring-necked Ducks (Conroy and Eberhardt 1983) (Table 14-1). In American Wigeon (Rienecker 1976) and Blue-winged Teal (L. D. Schroeder, unpubl. data), adult males showed higher survival rates than adult females in some areas but not in others. No difference in survival between sexes was found for Mottled Ducks (Johnson, Montalbano, and Hines 1984). The data sets for these latter three species were relatively small, however, which could account for the absence of significant differences. Among geese, there is little evidence of different survival rates for adult males and females (e.g. Stotts 1983), and sexes are generally pooled for survival rate estimation (Table 14-1).

Table 14-1. Annual survival rate estimates of North American Anatidae
Species/subspecies
Banding period
Banding years
Banding location
Sexa
Ageb
Annual survivalc
Source
Trumpeter SwanSummer1949-82MT
M&F
A
0.88
Anderson et al. 1986
White-fronted
     Goose
Preseason1967-69AK
M
F
A&S
A&S
0.70
0.65
Timm & Dau 1979
Canada Goose
    (primarily
    canadensis
    & interior)
    fulva
 
    interior
 
    leucopareia
 
    maxima
    moffitti
Preseason
 
 
 
Preseason
 
In season
 
Spring
 
Preseason
Preseason
1963-80
 
 
 
1956-60
 
1976-82
 
1976-79
 
1966-74
1953-73
Eastern North America (N.A.)
 
Glacier Bay, AK
WI
 
AK
 
MI
Western N.A.
M&F
M&F
 
 
M&F
 
M&F
M&F
M&F
 
M&F
M&F
M&F
A
Y
 
 
A
 
A
Y
A
 
A&Y
A
Y
0.70
0.60
 
 
0.84
 
0.77
0.64
0.77
 
0.75
0.64
0.53
Stotts 1983
 
 
 
Ratti et al. 1978
 
Samuel et al. 1986
Yparraguirre 1982
Tacha et al. 1980
Krohn & Bizeau 1980
Brant Summer 1956-75 Keewatin, N.W.T.
M&F
A
0.79
Kirby et al. 1986
Wood Duck Preseason 1960-68 Atlantic Flyway N.A.
M
M
F
F
A
Y
A
Y
0.54
0.44
0.49
0.42
F. A. Johnson et al. 1986
American Wigeon Winter 1951-69 CA
M
F
A
A
0.64
0.61
Rienecker 1976
Green-winged Teal Preseason 1955-61 Sask.
M
A
0.50
Martin et al. 1979
Mallard Preseason
 
Preseason
1969-81
 
1950-71
FL
 
N.A.
M&F
 
M
M
F
F
A&Y
 
A
Y
A
Y
0.37
 
0.63
0.50
0.56
0.50
Johnson et al. 1984
Anderson 1975b:22
Black Duck Preseason 1950-83 Eastern N.A.
M
M
F
F
A
Y
A
Y
0.63
0.48
0.47
0.38
Krementz et al. 1987
Northern Pintail Preseason 1948-79 CA
M
M
F
F
A
Y
A
Y
0.72
0.56
0.60
0.51
Rienecker 1987
Blue-winged Teal Preseason 1948-76 N.A.
M
M
F
F
A
Y
A
Y
0.59
0.44
0.52
0.32
L. D. Schroeder, unpubl. data
Canvasback Winter 1955-75 N.A.
M
F
A
A
0.76
0.61
Nichols & Haramis 1980
Ring-necked Duck Preseason 1966-76 Eastern N.A.
M
M
F
F
A
Y
A
Y
0.70
0.41
0.47
0.33
Conroy & Eberhardt 1983
aM = male, F = female.
bA = adult, S = subadult, Y = young.
cAll estimates except those for the leucopareia subspecies of the Canada Goose were obtained using band recovery data with the models of Brownie et al. (1985). The leucopareia estimates were obtained using resighting data in conjunction with the Jolly-Seber model (Seber 1982). All estimates represent arithmetic means over years and, in many cases, geographic areas.

Sex differences in survival appear to depend on the roles of the sexes in incubation and brood-rearing. For Mallards, and probably other ducks, very high mortality rates of hens during spring and summer are primarily responsible for the lower annual survival of females (Johnson and Sargeant 1977; Sargeant, Allen, and Eberhardt 1984; Cowardin, Gilmer, and Shaiffer 1985; Blohm et al. 1987). Among geese and swans, however, males generally remain in attendance at the nest and with the brood. Such nest- and brood-guarding likely reduces mortality risks to the female and results in similar nesting-season risks for both sexes. Hunting mortality rates also differ between the sexes in many species and may influence sex-specific survival differences (Johnson and Sargeant 1977).

Differences between sexes in annual survival rates tend to be less marked for young birds than adults, e.g., Wood Ducks (F. A. Johnson et al. 1986, Nichols and Johnson 1990), Mallards (Anderson 1975b), Black Ducks (Krementz et al. 1987), Pintails (Rienecker 1987), and Blue-winged Teal (L. D. Schroeder unpubl. report). Among young Ring-necked Ducks, Conroy and Eberhardt (1983) found instances of higher survival rates for males than females. For several duck species (see section III of this chapter), young birds make less reproductive effort than adults, so they may have reduced mortality risks, which are similar for young males and females, and higher breeding-season survival.

4. Condition and Social Status of the Bird

Physiological condition is commonly assumed to influence survival probability of birds, but until recently there have been few efforts to investigate such a relationship. Some relevant studies addressed mortality from all sources over a specified period, others addressed only hunting. Haramis et al. (1986) found evidence that early-winter body mass of adult male Canvasbacks was positively associated with the probability of surviving both the winter and the subsequent year. Pollock, Winterstein, and Conroy (1989) identified a positive relationship between condition indices of Black Ducks in early winter and their probabilities of surviving the winter. Reinecke, Shaiffer, and Delnicki (1987), on the other hand, found no consistent relation between body mass and overwinter survival probability of female Mallards in the Mississippi Alluvial Valley.

Investigating the effect of condition on vulnerability to hunting, Hepp et al. (1986) and Blohm et al. (1987) reported that banded Mallards with low condition indices in late fall showed higher probabilities of being shot and recovered during the subsequent hunting season. Greenwood, Clark, and Weatherhead (1986) found lower body weights for Mallards shot over decoys than those obtained by pass-shooting, suggesting that condition might affect susceptibility to certain kinds of hunting.

The relationship between social status and survival probability has been little studied in any bird species (Ketterson and Nolan 1983). Among waterfowl, behavioral dominance can lead to greater access to defendable food resources in some situations (Raveling 1970, Scott 1977, Alexander and Hair 1979, Patterson 1982), which conceivably could enhance survival. In the only test of this idea that we are aware of, Patterson (1982:75) found no consistent difference between the proportions of high- and low-ranking Northern Shelducks "disappearing" between years.

5. Geographic Variation

Annual survival probabilities within a species may vary geographically. Widely distributed species such as the Mallard provide good opportunities for testing general hypotheses about geographic variation. Anderson (1975b) and Nichols and Hines (1987) found small differences in survival rates of breeding and wintering Mallard populations in different areas of North America.

Black Duck breeding and wintering populations in the Lake Erie-Lake Ontario region tended to survive at a lower rate than those in other areas (Krementz et al. 1987), possibly because of changing land use patterns and competition with Mallards. Krementz et al. (1987) also noted that young Black Ducks seemed to exhibit greater geographic variation in survival rates than adults.

Lower survival rates for northern than southern Wood Duck populations were reported within both Mississippi (Bowers and Martin 1975) and Atlantic (F. A. Johnson et al. 1986) flyways. Nichols and Johnson (1990) speculated that these survival differences may be associated with the different migration habits and corresponding mortality risks of northern (migratory) versus southern (sedentary) Wood Ducks.

Nichols and Haramis (1980) found that female Canvasbacks wintering in a Delaware-Maryland-Virginia area exhibited lower survival rates than those wintering in California. Conroy and Eberhardt (1983) found lower survival probabilities for female Ring-necked Ducks banded in Mississippi Flyway wintering areas than for those banded on Atlantic Flyway wintering grounds; the reverse held for males.

6. Wetland Habitat and Weather

The relationship between survival probability and habitat quality is a topic of more discussion than research. J. D. Nichols, K. J. Reinecke, K. H. Pollock, and J. E. Hines (unpubl. data) found some evidence of a positive relationship between annual survival rate (August to August) of Mallards and wetland conditions (indexed by precipitation during the intervening November-January) in the Mississippi Alluvial Valley. Although Anderson (1975b) found no relation between the annual survival rate (August to August) of Mallards on prairie breeding grounds and the number of ponds during the intervening May in these areas, Nichols, Pospahala, and Hines (1982) did find some evidence of a positive relationship for male Mallards.

Seasonal, rather than annual, survival rate estimates provide better opportunities for investigating relationships between environmental variables and mortality risks, because annual rates are confounded by a variety of risks operating throughout the year. Reinecke, Shaiffer, and Delnicki (1987) found year-to-year variation in winter survival rates of Mallards in the Mississippi Alluvial Valley, with the highest survival rate occurring in a year of heavy winter rains (good water conditions) and mild temperatures; the lowest survival occurred during a year of favorable precipitation but freezing temperatures that prevented access to shallow water areas. Spring-summer survival rates for five years for Mallards in prairie habitat were not clearly related to May or July pond numbers (R. J. Blohm, R. E. Reynolds, and J. D. Nichols, unpubl. data).

Weather affects survival directly as well through its impact on habitat, it has direct effects as well. Severe winter weather may result in increased waterfowl mortality. The usual evidence provided in support of this relationship involves birds found dead following such weather events (e.g., Harrison and Hudson 1964).

7. Population Density

For many vertebrate populations, mortality rate is thought to vary directly as a function of density. Among waterfowl, the search for density-dependent survival rates has yielded mixed results. Anderson (1975b) found no relation between annual survival estimates and fall population size estimates for Mallards. J. D. Nichols, K. J. Reinecke, K. H. Pollock, and J. E. Hines (unpubl. data) found a negative association between annual survival rate estimates and indices to winter population size in their preliminary analyses with Mallards. Conroy and Eberhardt (1983) found a negative association between May population size estimates and annual survival rate estimates for male Ring-necked Ducks, but not for females.
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