Table 3.
Logistic regression model results assessing Imidacloprid detection probability for multiple variables in river otters collected in North Dakota, USA from 2015 to 2020
| Model | Variable | β | SE | P | n |
|---|---|---|---|---|---|
| Demographic | Intercept | -0.43 | 0.34 | 0.20 | 100 |
| Age | 0.06 | 0.08 | 0.43 | ||
| SexMale | -0.53 | 0.43 | 0.22 | ||
| Major Watershed | Intercept | -0.69 | 0.87 | 0.42 | 100 |
| James River | -15.87 | 2399.54 | 0.99 | ||
| Mouse River | -15.87 | 1696.73 | 0.99 | ||
| Red River | 0.13 | 0.89 | 0.89 | ||
| Minor Watershed | Intercept | -0.69 | 0.87 | 0.42 | 100 |
| Elm River | -17.87 | 2917.00 | 0.99 | ||
| Forest River | 1.10 | 1.26 | 0.38 | ||
| Goose River | 0.00 | 1.12 | 1.000 | ||
| James River | -17.87 | 6523.00 | 0.99 | ||
| Maple River | 0.29 | 1.08 | 0.79 | ||
| Park River | 1.61 | 1.20 | 0.18 | ||
| Pembina River | -17.87 | 2663.00 | 0.99 | ||
| Red River | -17.87 | 1883.00 | 0.99 | ||
| Sheyenne River | 0.69 | 0.96 | 0.47 | ||
| Souris River | -17.87 | 4612.00 | 0.99 | ||
| Turtle River | -0.69 | 1.41 | 0.62 | ||
| Wild Rice River | 1.20 | 1.13 | 0.29 | ||
| Distance to Water | Intercept | -1.22 | 0.28 | 0.000 | 100 |
| Distance | 0.83 | 0.26 | 0.002 | ||
| Date | Intercept | -2.61 | 1.21 | 0.03 | 100 |
| Julian Date | 0.04 | 0.01 | 0.004 | ||
| Julian Quadratic | 0.00 | 0.00 | 0.001 | ||
| Year | Intercept | 16.57 | 2399.54 | 0.99 | 100 |
| Year2017 | -17.34 | 2399.54 | 0.99 | ||
| Year2018 | -17.21 | 2399.54 | 0.99 | ||
| Year2019 | -16.94 | 2399.54 | 0.99 | ||
| Year2020 | -33.13 | 2938.83 | 0.99 |