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. 2011 Apr 10;10:81. doi: 10.1186/1475-2875-10-81

Table 1.

The abundance of early and late anopheline larvae in different habitat types in Fort Ternan, Lunyerere and Nyalenda during the two years of weekly sampling

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