Table 3.
Toxicity of tetrachlorvinphos to lesser mealworm adults from six strains
| Strain | n | LC50(µg cm−2) (95% CI) | LC95(µg cm−2) (95% CI) | RR50 a | RR95 b | Slope (SE) |
|---|---|---|---|---|---|---|
| Denmark‐S | 440 | 0.08 (0.07–0.10) | 0.23 (0.17–0.42) | — | — | 3.6 (0.6) |
| Kennebec | 690 | 1.26 (1.01–1.65)d | >1000 | 16* | >4000 | 1.5 (0.2)d |
| Waycrossc | 520 | 0.38 (0.31–0.49)d | >1000 | 4.8* | >4000 | 2.0 (0.2)d |
| Cayuga | 640 | 0.13 (0.09–0.20) | 0.73 (0.35–1.53) | 1.6 | 3.2 | 2.2 (0.5) |
| Onondaga | 580 | 0.18 (0.16–0.21) | 0.77 (0.58–1.17) | 2.3* | 3.4* | 2.6 (0.3) |
| Wayne | 590 | 0.34 (0.28–0.41) | 2.44 (1.69–4.18) | 4.3* | 11* | 1.9 (0.2) |
Resistance ratio at LC50 (i.e. LC50 resistant strain/LC50 Denmark‐S).
Resistance ratio at LC95 (i.e. LC95 resistant strain/LC95 Denmark‐S).
Cricket colony collection, all others (except Denmark‐S) are from caged‐layer poultry facilities.
Probit analysis was conducted using only the concentrations below the plateau of the line (see Fig. 1).
Significantly different from 1.0 based on non‐overlap of 95% CI.
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