Species
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Citation:
Author(s)
Goldberg, Stephen R.
Year
Exposure Endpoint Type |
Endpoint Value |
Endpoint Description |
Units |
Sex |
Life Cycle Stage |
Location |
Sample Size |
Type |
Time of Hatching or Parturition |
Aug. |
|
|
Not Reported |
Hatchling |
San Gabriel Mountains, Crystal Lake (elev., 1584 m) |
Not Reported |
Exposure Factor Datasets |
Body Weight - Mean |
15.3 |
average snout-vent length = 75mm |
g |
Not Reported |
Adult |
San Gabriel Mountains, Crystal Lake (elev., 1584 m) |
Not Reported |
Exposure Factor Datasets |
Body Weight - Mean |
11.1 |
average snout-vent length = 67mm |
g |
Not Reported |
Adult |
Puente Hills, Whittier (elev., 150 m) |
Not Reported |
Exposure Factor Datasets |
Time of Torpor or Hibernation |
Nov.-Feb. |
|
|
Not Reported |
Adult |
Puente Hills, Whittier (elev., 150 m) |
Not Reported |
Exposure Factor Datasets |
Time of Torpor or Hibernation |
Nov. - Mar. |
|
|
Not Reported |
Adult |
San Gabriel Mountains, Crystal Lake (elev., 1584 m) |
Not Reported |
Exposure Factor Datasets |
Clutches or Litters per year |
1-3 |
|
clutches/yr |
Female |
Adult |
Puente Hills, Whittier (elev., 150 m) |
Not Reported |
Exposure Factor Datasets |
Clutches or Litters per year |
1-2 |
|
clutches/yr |
Female |
Adult |
San Gabriel Mountains, Crystal Lake (elev., 1584 m) |
Not Reported |
Exposure Factor Datasets |
Citation:
Author(s)
Reynolds, Ronald E., Robert J. Blohm, James D. Nichols and James E. Hines
Year
Exposure Endpoint Type |
Endpoint Value |
Endpoint Description |
Error |
Sex |
Life Cycle Stage |
Location |
Sample Size |
Type |
Survival/ Mortality |
0.728 |
spring-summer survival (proportion) |
0.079 (SE) |
Female |
Yearling |
Alberta, Saskatchewan, Manitoba |
1,246 |
Exposure Factor Datasets |
Survival/ Mortality |
0.915 |
summer to spring survival (proportion) |
0.090 (SE) |
Female |
Adult |
Alberta, Saskatchewan, Manitoba |
11,139 |
Exposure Factor Datasets |
Citation:
Author(s)
Piccirillo, V.J. and R.P. Quesenberry
Year
Exposure Endpoint Type |
Endpoint Value |
Endpoint Description |
Sex |
Life Cycle Stage |
Sample Size |
Type |
Food Ingestion Rate |
574.7-1182.8 g/wk |
range of mean food consumption over the breeding period |
Both Male and Female |
Adult |
90 |
Exposure Factor Datasets |
Citation:
Author(s)
Arnold, T.W., M.D. Sorenson, and J.J. Rotella
Year
Exposure Endpoint Type |
Endpoint Value |
Endpoint Description |
Sex |
Life Cycle Stage |
Location |
Sample Size |
Type |
Hatching Success |
43.9% |
nest success rate (Mayfield method) among overwater nests |
Female |
Adult |
Minnedosa, Manitoba |
47 |
Exposure Factor Datasets |
Hatching Success |
12.2% |
nest success rate (Mayfield method) among upland nests |
Female |
Adult |
Minnedosa, Manitoba |
49 |
Exposure Factor Datasets |
Citation:
Author(s)
Gruenhagen, Ned. M. and Leigh H. Fredrickson
Year
Exposure Endpoint Type |
Endpoint Value |
Endpoint Description |
Sex |
Life Cycle Stage |
Location |
Sample Size |
Type |
Dietary Composition |
plant (82.9-98.4%), and invertebrates (1.6-17.1%) |
ranges of mean aggregate percent dry mass (stomach contents of ducks from different habitats) |
Female |
Both Adults and Juveniles |
Squaw Creek National Wildlife Refuge |
123 |
Exposure Factor Datasets |
Citation:
Author(s)
Leafloor, James O. and Bruce D.J. Batt
Year
Exposure Endpoint Type |
Endpoint Value |
Endpoint Description |
Sex |
Life Cycle Stage |
Sample Size |
Type |
Time of Molt |
July 21-27 |
mean annual date of molt initiation (over 3 yr) |
Male |
Adult |
126 |
Exposure Factor Datasets |
Time of Molt |
July 30-August 10 |
mean annual date of molt initiation (over 3 yr) |
Female |
Adult |
131 |
Exposure Factor Datasets |
Citation:
Author(s)
Heitmeyer, Mickey E., Daniel P. Connelly, and Roger L. Pederson
Publisher
Texas Tech University Press
Year
Exposure Endpoint Type |
Endpoint Value |
Endpoint Description |
Sex |
Life Cycle Stage |
Location |
Sample Size |
Type |
Population Density |
314,712 |
mean number of ducks counted in U.S. Fish and Wildlife Service mid-winter inventories 1978-1987 |
Both Male and Female |
Both Adults and Juveniles |
Sacramento Valley |
Not Reported |
Exposure Factor Datasets |
Population Density |
30,438 |
mean number of ducks counted in U.S. Fish and Wildlife Service mid-winter inventories 1978-1987 |
Both Male and Female |
Both Adults and Juveniles |
San Joaquin Valley |
Not Reported |
Exposure Factor Datasets |
Population Density |
15,221 |
mean number of ducks counted in U.S. Fish and Wildlife Service mid-winter inventories 1978-1987 |
Both Male and Female |
Both Adults and Juveniles |
Suisun Marsh |
Not Reported |
Exposure Factor Datasets |
Population Density |
4,667 |
mean number of ducks counted in U.S. Fish and Wildlife Service mid-winter inventories 1978-1987 |
Both Male and Female |
Both Adults and Juveniles |
San Francisco Delta |
Not Reported |
Exposure Factor Datasets |
Population Density |
389 |
mean number of ducks counted in U.S. Fish and Wildlife Service mid-winter inventories 1978-1987 |
Both Male and Female |
Both Adults and Juveniles |
Imperial and Coachella Valleys |
Not Reported |
Exposure Factor Datasets |
Citation:
Author(s)
Miller, A.W. and B.D. Collins
Year
Exposure Endpoint Type |
Endpoint Value |
Endpoint Description |
Units |
Sex |
Life Cycle Stage |
Location |
Sample Size |
Type |
Hatching Success |
85.2% |
proportion of observed nests with at least one successful hatch |
|
Female |
Adult |
Tule Lake and Lower Klamath River National Wildlife Refuges |
209 |
Exposure Factor Datasets |
Time of Nesting |
April-September |
period between first observed nest to last observed hatches |
|
Female |
Adult |
Tule Lake and Lower Klamath River National Wildlife Refuges |
209 |
Exposure Factor Datasets |
Clutch or Litter Size |
8.9 |
mean clutch size of successful nests |
eggs |
Female |
Adult |
Tule Lake and Lower Klamath River National Wildlife Refuges |
178 |
Exposure Factor Datasets |
Hatching Success |
91.4% |
Mean hatch success of successful nests |
|
Female |
Adult |
Tule Lake and Lower Klamath River National Wildlife Refuges |
178 |
Exposure Factor Datasets |
Time of Hatching or Parturition |
May-July |
|
|
Female |
Adult |
Tule Lake and Lower Klamath River National Wildlife Refuges |
Not Reported |
Exposure Factor Datasets |
Citation:
Author(s)
Yarris, Gregory S., M. Robert McLandress and Alison E.H. Perkins
Year
Exposure Endpoint Type |
Endpoint Value |
Endpoint Description |
Sex |
Life Cycle Stage |
Location |
Sample Size |
Type |
Time of Migration or Dispersal |
May 22 to July 10 |
timing of departure from breeding grounds |
Female |
Adult |
Suisun Marsh, Grizzly Island |
34 |
Exposure Factor Datasets |
Citation:
Author(s)
Combs, Daniel L. and Leigh H. Fredrickson
Year
Exposure Endpoint Type |
Endpoint Value |
Endpoint Description |
Sex |
Life Cycle Stage |
Location |
Sample Size |
Type |
Dietary Composition |
total plant seeds (19.3%), total grain (5.7%), acorns (64.5%), total vegetation (0.9%), tubers/rhizomes (5.1%), invertebrates (4.6%) |
mean aggregate % dry mass of foods collected in mallard stomachs (one season) |
Male |
Both Adults and Juveniles |
Mingo National Wildlife Refuge |
104 |
Exposure Factor Datasets |
Citation:
Author(s)
Smith, Kirtland G. and Harold H. Prince
Year
Exposure Endpoint Type |
Endpoint Value |
Endpoint Description |
Sex |
Life Cycle Stage |
Sample Size |
Type |
Metabolic Rate |
y = 1.970 - 0.054x (r-squared = 0.932) |
metabolic rate (ml O^2/g/h)-ambient temperature (celcius) relationship |
Male |
Juvenile |
20 |
Exposure Factor Datasets |
Metabolic Rate |
y = 1.780 - 0.052x (r-squared = 0.882) |
metabolic rate (ml O^2/g/h)-ambient temperature (celcius) relationship |
Female |
Juvenile |
20 |
Exposure Factor Datasets |
Citation:
Author(s)
Jarvis, Robert L., and Sean B. Furniss
Year
Exposure Endpoint Type |
Endpoint Value |
Endpoint Description |
Error |
Sex |
Life Cycle Stage |
Location |
Sample Size |
Type |
Survival/ Mortality |
0.377 |
estimated annual survival rate (1960-1971) |
0.046 (SE) |
Male |
Juvenile |
Malheur National Wildlife Refuge |
Not Reported |
Exposure Factor Datasets |
Survival/ Mortality |
0.628 |
estimated annual survival rate (1960-1971) |
0.035 (SE) |
Male |
Adult |
Malheur National Wildlife Refuge |
Not Reported |
Exposure Factor Datasets |
Survival/ Mortality |
0.569 |
estimated annual survival rate (1960-1971) |
0.105 (SE) |
Female |
Juvenile |
Malheur National Wildlife Refuge |
Not Reported |
Exposure Factor Datasets |
Survival/ Mortality |
0.586 |
estimated annual survival rate (1960-1971) |
0.081 (SE) |
Female |
Adult |
Malheur National Wildlife Refuge |
Not Reported |
Exposure Factor Datasets |
Citation:
Author(s)
Batt, Bruce D.J., and Harold H. Prince
Year
Exposure Endpoint Type |
Endpoint Value |
Endpoint Description |
Error |
Units |
Sex |
Life Cycle Stage |
Sample Size |
Type |
Clutch or Litter Size |
10.4 |
mean clutch size from first nesting attempt |
0.2 (SE) |
eggs |
Female |
Adult |
151 |
Exposure Factor Datasets |
Citation:
Author(s)
Clark, Jr., Donald R., Kevin S. Foerster, Carolyn M. Marn and Roger L. Hothem
Year
Exposure Endpoint Type |
Endpoint Value |
Endpoint Description |
Error |
Range |
Units |
Sex |
Life Cycle Stage |
Location |
Sample Size |
Type |
Clutch or Litter Size |
4.7 |
litter size estimated from counts of uterine scars and embryos |
0.7 SE |
3 - 7 |
#/litter |
Female |
Adult |
salt marsh, San Pablo and San Francisco Bays |
6 |
Exposure Factor Datasets |
Citation:
Author(s)
Brooks, G. R., Jr.
Year
Exposure Endpoint Type |
Endpoint Value |
Endpoint Description |
Units |
Sex |
Life Cycle Stage |
Location |
Sample Size |
Type |
Dietary Composition |
Insecta (51.8%); Arachnida (11.2%); Amphibia (2.8%); Diploda (1.3%); Gastropoda (1.3%); Crustacea (1.4%);Teleosts (1.1%); Mammalia (0.2%); Oligochaeta (1.3%); Reptilia (0.2%); Pebbles and sand (3.4%); Vegetative material (12.5%); Digested material (11.6%) |
% occurrence of item; obtained by dividing # of a specific item taken by total # of items; based on stomach contents |
|
Both Male and Female |
Both Adults and Juveniles |
ponds, Hanover County |
129 |
Exposure Factor Datasets |
Dietary Composition |
Insecta (20.6%); Arachnida (4.8%); Amphibia (27.4%); Diploda (0.3%); Gastropoda (1.0%); Crustacea (4.3%);Teleosts (0.6%); Mammalia (5.0%); Oligochaeta (1.3%); Reptilia (6.4%); Pebbles and sand (8.0%); Vegetative material (12.3%); Digested material (7.3%) |
% weight of an item; obtained by dividing the weight of a specific item by the total weight of all items; obtained from stomach contents |
|
Both Male and Female |
Both Adults and Juveniles |
ponds, Hanover County |
129 |
Exposure Factor Datasets |
Food Ingestion Rate |
0.4 |
average weight of stomach contents for frogs with an average body weight of 17.5 g |
g |
Both Male and Female |
Not Reported |
ponds, Hanover County |
78 |
Exposure Factor Datasets |
Food Ingestion Rate |
2.33 |
average weight of stomach contents for frogs with an average body weight of 106.3 g |
g |
Both Male and Female |
Not Reported |
ponds, Hanover County |
42 |
Exposure Factor Datasets |
Food Ingestion Rate |
4.6 |
average weight of stomach contents for frogs with an average body weight of 248.7 g |
g |
Both Male and Female |
Not Reported |
ponds, Hanover County |
18 |
Exposure Factor Datasets |
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