Northern Prairie Wildlife Research Center
| Parameter or variable name and levels | Value | Change from control (%) |
|---|---|---|
| Cropland to grassland ratioa | ||
| Control | 50:50 | |
| High | 100:0 | +100 |
| Low | 0:100 | -100 |
| Semipermanent basins with water (%) | ||
| Standardb | 65.0 |
|
| High | 87.0 |
+34 |
| Low | 34.7 |
-47 |
| Yearling (and adult) body weights (g) | ||
| Standard | 800 (900) |
|
| High | 860 (960) |
+6.9 |
| Low | 740 (840) |
-6.9 |
| Nest success (p)c | ||
| Standard | 0.135 |
|
| High | 0.633 |
-80d |
| Low | 0.039 |
+80 |
| Seasonal duckling survival rate for successful broods (p)c | ||
| Standard | 0.540 |
|
| High | 0.810 |
+50 |
| Low | 0.270 |
-50 |
| Brood survival rate (p)c | ||
| Standard | 0.740 |
|
| High | 0.920 |
+25 |
| Low | 0.550 |
-25 |
| a For the
cropland to grassland ratio the control was a plot with a 1:1 ratio
rather than the standard 1:0.57 ratio. b Standard values that represent favorable waterfowl habitat in central North Dakota. c Proportion = p. d To vary nest success, daily nest mortality rates were adjusted by ±80% in each habitat. |
||
| Habitat type | Relative availability (%) | Visual obstruction measurement ranges (dm)a |
Daily clutch mortality ratesa |
|---|---|---|---|
| Cropland (fall-plow grain) |
0.030 | 0.01-25.0 | 0.044-0.999 |
| Planted cover | 0.240 | 15.0-40.0 | 0.049 |
| Planted cover (burned) | 0.030 | 1.01-25.0 | 0.065-0.999 |
| Grassland (nongrazed) | 0.400 | 8.0-13.0 | 0.047 |
| Grassland (burned) | 0.080 | 0.01-13.0 | 0.047-0.999 |
| Other | 0.030 | 17.0-22.0 | 0.068 |
| Wetland (temporary) | 0.003(74)b | 12.0-17.0 | 0.070 |
| Wetland (seasonal) | 0.061(49) | 12.0-17.0 | 0.070 |
| Wetland (semipermanent) | 0.091(28) | 12.0-17.0 | 0.070 |
| Wetland (permanent) | 0.035(0) | 12.0-17.0 | 0.070 |
| a Values change
in response to phenological events or catastrophic events such as
burning or plowing. b Percentage of habitat available for nesting if <100 is placed in parentheses. |
|||
| Parameter | Definition | Input value | Source |
|---|---|---|---|
| H | Hatch time of clutch (days) | 31 |
Bellrose (1976) |
| INCTIME | Incubation of clutch (days) | 23 |
Bellrose (1976) |
| WTBAR(1) | Average weight of arriving yearling female pintails (grams) | 800 |
Bellrose (1976) |
| WTBAR(2) | Average weight of arriving adult female pintails (grams) | 900 |
Bellrose (1976) |
| CLUA | Intercept in regression equation to calculate clutch size with average equal to 7.75 eggs |
15.43 |
Bellrose (1976) |
| CLUB | Slope in regression equation to calculate clutch size |
0.063 |
Johnson et al.(1987) |
| ROBELA | Slope in regression equation to calculate nest site selection attractiveness based on VOMs of available habitats |
0.97 |
Calculated |
| ROBELB | Intercept (see ROBELA) | 0.28 |
Calculated |
| ROBLMIN | Intercept (see ROBELA) | 2.23 | Calculated |
| LOSSLAY | Weight lost per day during laying (grams) | 7.5 |
Scaled from |
| LOSSINC | Weight lost per day during incubation (grams) | 1.5 | Scaled from Johnson et al. (1987) |
| Mid-May | Mid-June | Average | |||||||
|---|---|---|---|---|---|---|---|---|---|
| Species | r 2 | N a | P b | r 2 | N | P | r 2 | N | P |
| Pintail | 0.55 | 8 | 0.04 | 0.61 | 7 | 0.04 | 0.64 | 7 | 0.03 |
| Mallard | 0.30 | 7 | 0.20 | 0.69 | 6 | 0.04 | 0.49 | 6 | 0.12 |
| a Number
of years in the regression. b Probability of a greater r2. |
|||||||||
| Parameter or variable
and percent change from control (%)a |
Recruitment rate | ||
|---|---|---|---|
| Averageb | SE | Change (%) | |
| Control | 0.439 | 0.004 | |
| Cropland to grassland ratio | |||
| 1:1 controlc | 0.478 | 0.050 | |
| 1:0 | 0.399 | 0.021 | -16.5 |
| 0:1 | 0.508 | 0.024 | +6.2 |
| Wetland condition | |||
| +34 | 0.484 | 0.039 | +10.2 |
| -47 | 0.251 | 0.011 | -42.8 |
| Yearling and adult body weight | |||
| +6.9 | 0.519 | 0.027 | +18.2 |
| -6.9 | 0.374 | 0.024 | -14.8 |
| Nest successd | |||
| -80 | 1.347 | 0.016 | +206.8 |
| +80 | 0.159 | 0.010 | -63.8 |
| Seasonal duckling survival rate for successful broods | |||
| +50 | 0.647 | 0.011 | +47.4 |
| -50 | 0.251 | 0.012 | -42.8 |
| Brood survival rate | |||
| +25 | 0.553 | 0.027 | +26.0 |
| -25 | 0.337 | 0.010 | -23.2 |
| a Controls
were standard values that represent favorable waterfowl habitat in
central North Dakota. b N = 4 simulations. c For cropland to grassland ratio the control ratio of 1:1 was used rather than the standard control ratio of 1:0.57. d To vary nest success, daily clutch mortality rates were adjusted by ±80% in each habitat. |
|||
| Parameter or variable | F valuea | Parameter variable | F valuea |
| Nest success | 100,000 |
Seasonal duckling survival rate × brood survival rate |
3,102 |
| Seasonal duckling survival rate | 61,367 |
||
| Nest success × seasonal duckling survival rate |
40,510 |
Yearling and adult body weight × seasonal duckling survival rate |
2,139 |
| Brood survival rate | 14,693 |
Nest success × seasonal duckling survival rate × brood survival rate |
2,047 |
| Wetland condition | 10,032 |
||
| Nest success × brood survival rate | 9,846 |
Wetland condition × nest success × seasonal duckling survival rate |
1,732 |
| Yearling and adult body weight | 7,039 |
||
| Wetland condition × nest success | 5,323 |
Yearling and adult body weight × nest success × seasonal duckling survival rate |
1,141 |
| Yearling and adult body weight × nest success |
3,753 |
||
| Wetland condition × seasonal duckling survival rate |
3,156 |
Cropland to grassland ratio | 1,011 |
| a 1 df. | |||
| Source | Wetland conditions | Comparisons N |
Average pairs |
Average nest initiations |
Average successful nests |
|---|---|---|---|---|---|
| Observed |
Wet |
3 | 36.0 | 20.3 | 9.3 |
| Simulated |
Wet |
3 | 36.0 | 72.3a | 12.3 |
| Observed |
Average |
4 | 34.2 | 20.8 | 10.2 |
| Simulated |
Average |
4 | 34.2 | 64.2a | 10.5 |
| Observed |
Dry |
3 | 17.0 | 11.7 | 4.0 |
| Simulated |
Dry |
3 | 17.0 | 18.3 | 3.6 |
| a Significantly different from observed data (P < 0.01). | |||||
| Wetland conditions | Recruitment rate | ||
|---|---|---|---|
| Averagea | SE | Change (%) | |
| Wet | 0.701 | 0.022 | +18.2 |
| Average | 0.624 | 0.036 | +21.6 |
| Dry | 0.365 | 0.006 | +15.5 |
| a N = 4 simulations. | |||