Institut de Recherche pour le Développement (IRD), UMR MIVEGEC (CNRS/IRD/UM): Maladies Infectieuses et Vecteurs: Ecologie, Génétique, Evolution et Contrôle, Montpellier, France.
IRD Réunion/GIP CYROI (Recherche Santé Bio-innovation), Sainte Clotilde, Reunion Island, France.
Parasit Vectors. 2019 Feb 12;12(1):81. doi: 10.1186/s13071-019-3329-7.
To develop an efficient sterile insect technique (SIT) programme, the number of sterile males to release, along with the spatial and temporal pattern of their release, has to be determined. Such parameters could be estimated from a reliable estimation of the wild population density (and its temporal variation) in the area to treat. Here, a series of mark-release-recapture experiments using laboratory-reared and field-derived Aedes albopictus males were carried out in Duparc, a selected pilot site for the future application of SIT in the north of La Reunion Island.
The dispersal, longevity of marked males and seasonal fluctuations in the population size of native mosquitoes were determined from the ratio of marked to unmarked males caught in mice-baited BG-Sentinel traps. The study was conducted during periods of declining population abundance (April), lowest abundance (September) and highest abundance (December).
According to data collected in the first 4 days post-release, the Lincoln index estimated population size as quite variable, ranging from 5817 in April, to 639 in September and 5915 in December. Calculations of daily survival probability to 4 days after release for field and laboratory males were 0.91 and 0.98 in April, respectively, and 0.88 and 0.84 in September, respectively. The mean distance travelled (MDT) of released field males were 46 m, 67 m and 37 m for December, April and September experiments, respectively. For released laboratory males, the MDT was 65 m and 42 m in April and September, respectively.
Theoretically, the most efficient release programme should be started in July/August when the mosquito population size is the lowest (c.600 wild males/ha relative to 5000 wild males estimated for December and April), with a weekly release of 6000 males/ha. The limited dispersal of Ae. albopictus males highlights the nessecity for the widespread release of sterile males over multiple sites and in a field setting to avoid topographical barriers and anthropogenic features that may block the migration of the released sterile male mosquitoes.
为了开发高效的无菌昆虫技术(SIT)项目,必须确定要释放的无菌雄虫数量以及它们释放的时空模式。这些参数可以通过对要处理的区域内野生种群密度(及其时间变化)的可靠估计来估计。在这里,在留尼汪岛北部选定的 SIT 应用试点 Duparc 进行了一系列使用实验室饲养和野外来源的白纹伊蚊雄蚊的标记释放-回收实验。
通过在 BG-Sentinel 诱捕器中捕获的有标记和无标记的雄性比例,确定标记雄性的扩散、寿命和本地蚊子种群数量的季节性波动。该研究在种群数量下降(4 月)、最低数量(9 月)和最高数量(12 月)期间进行。
根据释放后前 4 天收集的数据,林肯指数估计种群规模变化较大,4 月为 5817,9 月为 639,12 月为 5915。实验室和野外雄蚊释放后 4 天的日生存概率分别为 0.91 和 0.98,9 月分别为 0.88 和 0.84。释放的野外雄蚊的平均移动距离(MDT)分别为 12 月、4 月和 9 月实验的 46m、67m 和 37m,释放的实验室雄蚊的 MDT 分别为 4 月和 9 月的 65m 和 42m。
理论上,当蚊子种群数量最低(估计 12 月和 4 月为 5000 只野生雄性,而 6 月为 600 只野生雄性)时,应在 7 月/8 月开始最有效的释放计划,每周释放 6000 只雄性/公顷。白纹伊蚊雄蚊的扩散能力有限,突出表明需要在多个地点和野外环境中广泛释放不育雄蚊,以避免可能阻止释放的不育雄蚊迁移的地形障碍和人为特征。