| Literature DB >> 31549615 |
Béatrice Gaillard1,2, Fréderic Simard1, Laurent Dormont2, Pierre Jay-Robert2, Denis D'Abadie de Lurbe3, Manuel Etienne3, Anne Baudin4, Jocelyn Raude5.
Abstract
Perceived exposure to mosquitoes plays a fundamental role in the adoption of a range of protective behaviors aiming to prevent and control mosquito-borne disease. However, it is largely unknown in the present literature to what extent perceived exposure is associated with actual exposure. Moreover, the perception of nuisance may depend on the natural environment in which human populations are living, and especially its epidemiological context. In this study, the hypothesis that perceived exposure is driven by mosquito abundance was tested in two different geographic areas. We compared a range of perceived nuisance measures-collected through questionnaires-with egg number measured within ovitraps located in the south of France, which has been recently colonized by an arbovirus vector, and La Martinique island, a tropical French territory, which has a long history of outbreaks of mosquito-borne pathogens. Unexpectedly, only the nuisance due to mosquito noise was correlated with ovitrap activity in southern France. All other perceived exposure measures, both in the south of France and in Martinique, were not correlated with egg number surrounding households investigated. These results suggest the existence of habituation effects that may disturb the engagement in adaptive behaviors in the face of change in the entomological conditions.Entities:
Mesh:
Year: 2019 PMID: 31549615 PMCID: PMC6838563 DOI: 10.4269/ajtmh.19-0074
Source DB: PubMed Journal: Am J Trop Med Hyg ISSN: 0002-9637 Impact factor: 2.345
P-values of Pearson correlation between nuisance measure and number of eggs measured within the nearest ovitraps in Martinique
| Nuisance due to mosquitoes outside | Nuisance due to mosquito bites | Nuisance due to night noise | Nuisance due to the requirement to remove stagnant water | Nuisance due to mosquito presence | Composite index | |
|---|---|---|---|---|---|---|
| January 1 | 0.367 | 0.401 | 0.978 | 0.727 | 0.562 | 0.543 |
| January 20 | 0.945 | 0.592 | 0.520 | 0.380 | 0.818 | 0.784 |
| February 1 | 0.994 | 0.958 | 0.863 | 0.671 | 0.435 | 0.612 |
| February 20 | 0.784 | 0.867 | 0.906 | 0.577 | 0.462 | 0.853 |
| March 1 | 0.0942 | 0.259 | 0.536 | 0.742 | 0.122 | 0.676 |
| March 20 | 0.734 | 0.732 | 0.163 | 0.340 | 0.767 | 0.312 |
| April 1 | 0.630 | 0.837 | 0.799 | 0.512 | 0.610 | 0.578 |
| Total | 0.803 | 0.706 | 0.728 | 0.877 | 0.901 | 0.891 |
P-values of Pearson correlation between nuisance measure and number of eggs measured within the nearest ovitraps in the south of France
| Nuisance due to mosquitoes outside | Nuisance due to mosquito bites | Nuisance due to night noise | Nuisance due to the requirement to remove stagnant water | Nuisance due to mosquito presence | Composite index | |
|---|---|---|---|---|---|---|
| May 12 | 0.902 | 0.335 | 0.534 | 0.771 | 0.717 | 0.682 |
| May 24 | 0.011 | 0.789 | 0.490 | 0.912 | 0.041 | 0.034 |
| June 8 | 0.812 | 0.707 | 0.126 | 0.693 | 0.567 | 0.323 |
| June 22 | 0.308 | 0.909 | 0.0497 | 0.469 | 0.904 | 0.481 |
| July 5 | 0.340 | 0.576 | 0.489 | 0.626 | 0.617 | |
| July 21 | 0.240 | 0.150 | 0.247 | 0.089 | 0.092 | |
| August 3 | 0.767 | 0.454 | 0.001 | 0.289 | 0.109 | 0.641 |
| August 17 | 0.007 | 0.034 | 0.335 | 1.75e-3 | 0.062 | 0.020 |
| August 31 | 0.132 | 7.37e-4 | 0.020 | 0.049 | 0.039 | |
| September 14 | 0.097 | 0.839 | 0.425 | 0.706 | 0.205 | 0.573 |
| September 28 | 0.017 | 0.389 | 0.790 | 0.838 | 0.035 | 0.836 |
| October 12 | 0.036 | 0.676 | 0.001 | 1.73e-3 | 0.680 | 0.531 |
| Total | 0.238 | 0.315 | 0.254 | 0.778 | 0.214 |
Bold values represent significant correlations with a threshold at 6.41e-4 (after Bonferroni correction).