Table 1.
Site name | Habitat type | Habitat stability | Weekly sampling (%) | Early instars | Late instars | ||||
---|---|---|---|---|---|---|---|---|---|
(EMM ± SE) | OR | P | (EMM ± SE) | OR | P | ||||
Fort Ternan | Rain pools | Temporary | 4.4 | 0.060 ± 0.019 | 1 | 0.037 ± 0.009 | 1 | ||
Drainage canal | Permanent | 14 | 0.036 ± 0.012 | 0.666 | 0.054** | 0.036 ± 0.006 | 0.976 | 0.918 | |
Erosion pit | Permanent | 17.7 | 0.102 ± 0.009 | 1.390 | 0.090 | 0.040 ± 0.004 | 0.913 | 0.676 | |
Hoof print | Temporary | 13.6 | 0.131 ± 0.013 | 1.991 | 0.001* | 0.069 ± 0.006 | 1.753 | 0.007* | |
River fringe | Permanent | 11.1 | 0.060 ± 0.019 | 0.641 | 0.052** | 0.024 ± 0.006 | 0.412 | 0.002* | |
Taps | Permanent | 25.9 | 0.043 ± 0.010 | 0.431 | 0.000* | 0.020 ± 0.005 | 0.325 | 0.000* | |
Tire track | Temporary | 13.4 | 0.052 ± 0.013 | 0.896 | 0.690 | 0.028 ± 0.006 | 0.797 | 0.327 | |
Lunyerere | Rain pools | Temporary | 1.5 | 0.124 ± 0.056 | 1 | 0.035 ± 0.023 | 1 | ||
Drainage canal | Permanent | 89.2 | 0.167 ± 0.007 | 1.134 | 0.648 | 0.062 ± 0.003 | 1.249 | 0.535 | |
Erosion pit | Permanent | 6.7 | 0.129 ± 0.027 | 1.019 | 0.956 | 0.046 ± 0.011 | 1.214 | 0.635 | |
Hoof print | Temporary | 2.5 | 0.014 ± 0.044 | 0.234 | 0.069 | 0.006 ± 0.018 | 0.133 | 0.022* | |
Container | Temporary | 0.2 | 0.020 ± 0.176 | 1.000 | - | 0.012 ± 0.072 | 1.000 | - | |
Nyalenda | Rain pools | Temporary | 2.3 | 0.058 ± 0.033 | 1 | 0.002 ± 0.007 | 1 | ||
Drainage canal | Permanent | 56.1 | 0.076 ± 0.11 | 1.624 | 0.255 | 0.014 ± 0.002 | 2.118 | 0.195 | |
Hoof print | Temporary | 1.1 | 0.042 ± 0.047 | 0.692 | 0.488 | 0.000 ± 0.010 | 0.446 | 0.312 | |
Rice paddy | Temporary | 39.5 | 0.135 ± 0.013 | 2.586 | 0.026* | 0.014 ± 0.003 | 3.164 | 0.048* | |
Burrow pit | Permanent | 1.0 | 0.366 ± 0.48 | 7.302 | 0.003* | 0.038 ± 0.010 | 7.781 | 0.010* |
*Significantly different from rain pools **marginally significant from rain pools at P = 0.05, OR = Odds ratio; P = level of significance; EMM = estimated marginal means; SE = standard error of the mean