Table 1 |
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Algorithms used to predict the occurrence of Canadian census sub-divisions containing resident I. scapularis populations. |
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| Algorithm |
AUC |
SE |
95% CI |
AIC |
|
|
|
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| 1 |
No. of ticks at model equilibrium (T) |
0.921 |
0.030 |
0.863 – 0.979 |
214 |
| 2 |
No. of ticks at model equilibrium categorised (Tc) |
0.780 |
0.052 |
0.678 – 0.881 |
206 |
| 3 |
Percent forest area (F) |
0.387 |
0.038 |
0.313 – 0.461 |
232 |
| 4 |
Index of larval tick immigration (range 255 km: IL) |
0.816 |
0.052 |
0.713 – 0.919 |
211 |
| 5 |
Index of nymphal tick immigration (range 425 km: IN) |
0.896 |
0.025 |
0.848 – 0.949 |
216 |
| 6 |
T * IN |
0.926 |
0.029 |
0.869 – 0.983 |
180 |
| 7 |
Tc * IN |
0.807 |
0.055 |
0.699 – 0.914 |
183 |
| 8 |
T * IL |
0.845 |
0.052 |
0.743 – 0.947 |
207 |
| 9 |
Tc * IL |
0.723 |
0.056 |
0.614 – 0.832 |
207 |
| 10 |
T * IN * (0.05* IL)† |
0.926 |
0.029 |
0.869 – 0.983 |
1851 |
| 11 |
Tc * IN * (0.05* IL)† |
0.807 |
0.055 |
0.699 – 0.914 |
1861 |
| 12 |
T * IN* F |
0.821 |
0.050 |
0.723 – 0.919 |
1852 |
| 13 |
Tc * IN* F |
0.752 |
0.054 |
0.646 – 0.858 |
1862 |
| 14 |
T * IN* Log10 F |
0.832 |
0.051 |
0.732 – 0.933 |
1852 |
| 15 |
Tc * IN* Log10 F |
0.762 |
0.056 |
0.652 – 0.871 |
1872 |
|
|
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†Larva-to-nymph survival of I. scapularis is approximately one twentieth of nymph-to-adult survival (Ogden et al., 2005). 1 In all logistic regression models containing variables relating to forest cover, these variables were not significant. 2 In neither of these models was the variable (0.05* IL) significant. The performance of different risk algorithms in ROC analysis is shown: AUC = area under the ROC curve, SE = standard error, 95% CI = 95% confidence interval for AUC. AIC = Aikeke's Information criterion of a logistic regression model for each algorithm in which the outcome was the occurrence of a known I. scapularis population, and the explanatory variables were the algorithm component(s). |
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Ogden et al. International Journal of Health Geographics 2008 7:24 doi:10.1186/1476-072X-7-24 |
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