| Literature DB >> 27519419 |
Yiji Li1, Xinghua Su1, Guofa Zhou2, Hong Zhang1, Santhosh Puthiyakunnon1, Shufen Shuai1, Songwu Cai3, Jinbao Gu1, Xiaohong Zhou1, Guiyun Yan1,2, Xiao-Guang Chen4.
Abstract
BACKGROUND: The surveillance of vector mosquitoes is important for the control of mosquito-borne diseases. To identify a suitable surveillance tool for the adult dengue vector Aedes albopictus, the efficacy of the BG-Sentinel trap, CDC light trap and Mosquito-oviposition trap (MOT) on the capture of vector mosquitoes were comparatively evaluated in this study.Entities:
Keywords: Aedes albopictus; Anopheles sinensis; BG-Sentinel trap; CDC light trap; Culex quinquefasciatus; Mosq-ovitrap; Surveillance
Mesh:
Year: 2016 PMID: 27519419 PMCID: PMC4983048 DOI: 10.1186/s13071-016-1724-x
Source DB: PubMed Journal: Parasit Vectors ISSN: 1756-3305 Impact factor: 3.876
Fig. 1Map of the study areas and distribution of the traps in the first week of each month. a Liangtian (suburban area), b Tonghe (urban area). Twelve each of BGS Traps, CDC Light Traps and MOTs were used to survey the mosquito density in Tonghe and Liangtian
Fig. 2The effectiveness of the three kinds of traps in catching different species of mosquitoes in laboratory conditions. Comparative analysis of mean and standard error of Aedes albopictus, Cx. quinquefasciatus and An. sinensis caught in different traps under laboratory conditions. Columns with different letters are significantly different from each other (P < 0.05). Mosquito abundance is square-root transformed, and values are the mean ± standard error
Sex differences among mosquitoes collected in the three mosquito traps in the laboratory
| Traps | No. of release times |
|
|
| |||
|---|---|---|---|---|---|---|---|
| Male | Female | Male | Female | Male | Female | ||
| BGS trap | 8 | 7.59 ± 0.20a | 8.78 ± 0.17b | 7.50 ± 0.19a | 8.65 ± 0.22b | 1.26 ± 0.31a | 1.53 ± 0.24a |
| CDC Light trap | 8 | 3.30 ± 0.27a | 3.15 ± 0.16a | 4.09 ± 0.24a | 3.29 ± 0.41a | 4.77 ± 0.44a | 3.23 ± 0.25b |
| Mosq-ovitrap | 8 | 3.70 ± 0.31a | 0.78 ± 0.24b | 0.48 ± 0.36a | 0.43 ± 0.31a | 0.11 ± 0.13a | 0.13 ± 0.13a |
Rows with different letters are significantly different from each other (P < 0.05). Mosquito abundance is square-root transformed and values are the mean ± standard error
Abbreviations: M male, F female
Species and sex composition of mosquitoes collected in BG-Sentinel and CDC light traps in Guangzhou, China
| Study area | Species | Trap method | Sex ratio difference ( | |||||||
|---|---|---|---|---|---|---|---|---|---|---|
| BG-sentinel trap | CDC light trap | |||||||||
| Total | Male | Female | F rate (95 % CI)a | Total | Male | Female | F rate (95 % CI)a | |||
| Tonghe (urban) | Number of trap days | 864 | 864 | |||||||
|
| 6211 | 3641 | 2570 | 0.41 [0.40, 0.43] | 1389 | 790 | 599 | 0.43 [0.41, 0.46] | 0.23 | |
|
| 11,365 | 7588 | 3777 | 0.33 [0.32, 0.34] | 8071 | 4758 | 3313 | 0.41 [0.40, 0.42] | < 0.0001 | |
|
| 46 | 25 | 21 | 0.46 [0.32, 0.60] | 83 | 49 | 34 | 0.41 [0.31, 0.52] | 0.60 | |
|
| 1 | 1 | 0 | n.a. | 8 | 5 | 3 | 0.38 [0.14, 0.69] | n.a. | |
| Total No. | 17,623 | 11,255 | 6368 | 9551 | 5602 | 3951 | ||||
| Liangtian (suburban) | Number of trap days | 876 | 864 | |||||||
|
| 2181 | 1200 | 981 | 0.45 [0.43, 0.47] | 385 | 195 | 190 | 0.49 [0.44, 0.54] | 0.11 | |
|
| 18,442 | 12,517 | 5925 | 0.32 [0.31, 0.33] | 31,288 | 16,233 | 15,055 | 0.48 [0.48, 0.49] | < 0.0001 | |
|
| 152 | 91 | 61 | 0.40 [0.33, 0.48] | 184 | 114 | 70 | 0.38 [0.31, 0.45] | 0.70 | |
|
| 3 | 1 | 2 | 0.67 [0.21, 0.94] | 14 | 10 | 4 | 0.29 [0.12, 0.55] | 0.51 | |
| Total No. | 20,778 | 13,809 | 6969 | 31,871 | 16,552 | 15,319 | ||||
aF rate is defines as number of females over total
bDifference between the two trap-types. χ 2-test or Fisher exact test if any number is < 5
Fig. 3Population dynamics of Aedes albopictus and Cx. quinquefasciatus collected by two traps in urban and suburban areas. a and c Tonghe (urban). b and d Liangtian (suburban). a and b: Ae. albopictus; c and d: Cx. quinquefasciatus. Values are the mean ± 95 % CI
Results of negative binomial regression analysis in the field study
| Species | Coefficients | Estimate | Std. Error |
| Pr(>|z|) |
|---|---|---|---|---|---|
|
| |||||
| (Intercept) | -6.11 | 0.18 | -34.14 | < 0.0001 | |
| Site (urban) | 0.85 | 0.05 | 15.91 | < 0.0001 | |
| TrapType (CDC) | -1.88 | 0.07 | -25.13 | < 0.0001 | |
| Site (urban) * TrapType (CDC) | 0.51 | 0.09 | 5.41 | < 0.0001 | |
| Month | 2.07 | 0.05 | 42.20 | < 0.0001 | |
| Month*Month | -0.13 | 0.003 | -41.18 | < 0.0001 | |
|
| |||||
| (Intercept) | 2.88 | 0.06 | 44.85 | < 0.0001 | |
| Site (urban) | -0.24 | 0.05 | -5.24 | < 0.0001 | |
| TrapType (CDC) | 0.62 | 0.05 | 13.85 | < 0.0001 | |
| Site(urban) * TrapType(CDC) | -0.88 | 0.06 | -13.62 | < 0.0001 | |
| Month | -0.28 | 0.02 | -13.48 | < 0.0001 | |
| Month*Month | 0.03 | 0.002 | 19.86 | < 0.0001 | |