From: Ecological drivers of dog heartworm transmission in California
 | Northern California | Central California | Southern California | ||||||
---|---|---|---|---|---|---|---|---|---|
 | Coef. estimate | Std. error | p-value | Coef. estimate | Std. error | p-value | Coef. estimate | Std. error | p-value |
Ae. aegypti | −69.392 | 44.763 | 0.124 | 7.697 | 2.899 | 0.010* | 26.229 | 13.939 | 0.070 |
Ae. albopictus | −1368.483 | 486.612 | 0.006* | NA | NA | NA | 35.1330 | 12.444 | 0.008* |
Ae. sierrensis | 4.607 | 12.626 | 0.716 | 4.003 | 1.951 | 0.045* | −20.068 | 9.353 | 0.040* |
Ae. vexans | 12.912 | 17.754 | 0.469 | 3.258 | 1.869 | 0.087 | −19.892 | 8.554 | 0.027* |
An. freeborni | 0.182 | 12.917 | 0.989 | 0.143 | 2.108 | 0.946 | −8.314 | 8.373 | 0.329 |
Cs. incidens | 34.238 | 11.822 | 0.005* | 8.968 | 3.152 | 0.006* | −0.336 | 9.536 | 0.972 |
Cs. inornata | 2.829 | 11.388 | 0.804 | −0.027 | 2.007 | 0.989 | −18.527 | 15.271 | 0.235 |
Cx. quinquefasciatus | −20.712 | 10.901 | 0.060 | 3.219 | 2.619 | 0.224 | −30.629 | 15.727 | 0.061 |
Cx. tarsalis | −25.425 | 11.206 | 0.025* | −0.965 | 2.487 | 0.699 | −4.221 | 16.298 | 0.797 |
Dog density | −0.874 | 8.092 | 0.914 | −13.899 | 4.077 | 0.001* | 62.701 | 20.786 | 0.005* |
Income | −10.128 | 16.388 | 0.538 | 9.784 | 5.789 | 0.097 | −81.849 | 16.851 |  < 0.001* |
Full model | \({R}^{2}\)= 0.505 | \({R}^{2}\)= 0.720 | \({R}^{2}\)= 0.874 | ||||||
Year and bioregion dummy variables only | \({R}^{2}\)= 0.409 | \({R}^{2}\)= 0.499 | \({R}^{2}\)= 0.598 | ||||||
Year dummy variable only | \({R}^{2}\)= 0.405 | \({R}^{2}\)= 0.492 | \({R}^{2}\)= 0.503 | ||||||
Bioregion dummy variable only | \({R}^{2}\)= 0.401 | \({R}^{2}\)= 0.505 | \({R}^{2}\)= 0.617 |