| Literature DB >> 34240181 |
Kyran M Staunton1,2, Joelyn Goi3, Michael Townsend1,2, Scott A Ritchie1,2, Jacob E Crawford4, Nigel Snoad4, Stephan Karl2,3, Thomas R Burkot2.
Abstract
With global expansion of the two main vectors of dengue, Aedes aegypti (Linnaeus, Diptera: Culicidae) and Aedes albopictus (Skuse, Diptera: Culicidae), there is a need to further develop cost-effective and user-friendly surveillance tools to monitor the population dynamics of these species. The abundance of Ae. aegypti and Ae. Albopictus, and associated bycatch captured by Male Aedes Sound Traps (MASTs) and BG-Sentinel (BGS) traps that were unbaited or baited with BG-Lures were compared in Cairns, Australia and Madang, Papua New Guinea. Mean male Ae. aegypti and Ae. albopictus catch rates in MASTs did not significantly differ when deployed with BG-Lures. Similarly, males of both these species were not sampled at statistically different rates in BGS traps with or without BG-Lures. However, MASTs with BG-Lures caught significantly less male Ae. aegypti than BGS traps baited with BG-Lures in Cairns, and MASTs without BG-Lures caught significantly more male Ae. albopictus than BGS traps without BG-Lures in Madang. Additionally, BG-Lures significantly increased female Ae. aegypti catch rates in BGS traps in Cairns. Lastly, bycatch capture rates in BGS traps were not significantly influenced by the addition of the BG-Lures. While this study provides useful information regarding the surveillance of Ae. aegypti and Ae. albopictus in these locations, further development and investigation is required to successfully integrate an olfactory lure into the MAST system.Entities:
Keywords: zzm321990 Aedes aegyptizzm321990 ; zzm321990 Aedes albopictuszzm321990 ; dengue; mosquito trap; sound lure
Mesh:
Year: 2021 PMID: 34240181 PMCID: PMC8577766 DOI: 10.1093/jme/tjab121
Source DB: PubMed Journal: J Med Entomol ISSN: 0022-2585 Impact factor: 2.278
Fig. 1.Mean abundance of male Ae. aegypti in the Semi-field cage for comparisons between (A) the unbaited MAST Spray and the MAST Spray with the BG-Lure on top of the MAST capture chamber (n = 24), (B) the unbaited MAST Spray and the MAST Spray with the BG-Lure inside the MAST capture chamber (n = 21) and (C) the unbaited MAST Sticky and the MAST Sticky with the BG-Lure inside the MAST capture chamber (n = 24). Different letters above points indicate significantly different groups (analysis of deviance, P < 0.05).
Summary data of all taxa caught in Cairns, Australia and Madang, PNG
| Cairns, Australia | Madang, PNG | |||||||
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| 254 | 400 | 285 | 184 | 27 | 23 | 43 | 14 |
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| 292 | 471 | 1 | 0 | 67 | 46 | 0 | 0 |
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| 0 | 0 | 0 | 0 | 44 | 102 | 172 | 115 |
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| 0 | 0 | 0 | 0 | 250 | 300 | 0 | 0 |
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| 6 | 2 | 0 | 0 | 0 | 0 | 0 | 0 |
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| 0 | 0 | 0 | 0 | 1 | 1 | 0 | 0 |
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| 69 | 98 | 9 | 7 | 1,411 | 1,158 | 2 | 2 |
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| 91 | 89 | 0 | 0 | 1,025 | 926 | 0 | 0 |
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| 0 | 0 | 0 | 0 | 1 | 9 | 0 | 0 |
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| 3 | 4 | 0 | 0 | 0 | 0 | 0 | 0 |
| Diptera (other) | 774 | 908 | 0 | 5 | 4,043 | 5,195 | 9 | 49 |
| Hemiptera | 1 | 4 | 0 | 0 | 740 | 606 | 4 | 0 |
| Lepidoptera | 270 | 271 | 0 | 0 | 393 | 266 | 2 | 1 |
| Hymenoptera (winged) | 19 | 28 | 0 | 1 | 158 | 214 | 4 | 0 |
| Formicidae | 7 | 13 | 0 | 1 | 84 | 197 | 7 | 1 |
| Coleoptera | 26 | 17 | 0 | 0 | 121 | 138 | 0 | 2 |
| Collembola | 2 | 2 | 0 | 0 | 96 | 93 | 0 | 1 |
| Araneae | 17 | 11 | 0 | 0 | 27 | 24 | 1 | 0 |
| Blattodea | 1 | 1 | 0 | 0 | 25 | 23 | 0 | 0 |
| Orthoptera | 0 | 0 | 0 | 0 | 2 | 0 | 0 | 0 |
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Fig. 2.Weekly catch rates of (A) male Ae. aegypti in Cairns and (B) male Ae. albopictus in Madang. Different letters above points indicate significantly different groups (Tukey HSD, P < 0.05; n = 24). MAST captures in Cairns and Madang were made using MAST Spray and MAST Sticky trap versions, respectively.
BG-Lure influence on catches of other taxa of interest (analysis of variance)
| Taxa | BGS trap mean ± (S.E.) | BGS trap + BG-Lure mean ± (S.E.) | χ2 | df |
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| Cairns |
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| 2.8 (1.2) | 4.1 (1.5) | 0.08 | 1 | 0.77 | |
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| 3.8 (1.5) | 3.7 (1.6) | 1.28 | 1 | 0.26 | |
| Diptera (non-mosquito) | 32.3 (10.4) | 37.8 (7.3) | 0.79 | 1 | 0.37 | |
| All non-dipteran bycatch | 14.2 (2.7) | 14.3 (1.3) | 0.30 | 1 | 0.59 | |
| Madang |
| 10.9 (2.2) | 13.6 (5.4) | 1.55 | 1 | 0.21 |
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| 61.4 (22.6) | 52.6 (14.5) | 0.14 | 1 | 0.71 | |
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| 44.6 (11.3) | 42.1 (11.7) | 0.02 | 1 | 0.89 | |
| Diptera (non-mosquito) | 175.8 (22.6) | 236.1 (36.2) | 3.51 | 1 | 0.06 | |
| All non-dipteran bycatch | 71.5 (8.9) | 71 (11.0) | 0.73 | 1 | 0.39 |
The group determined to be significantly different (P ≤ 0.05, n = 24) is in boldface type.