Yale School of Public Health, Yale University, New Haven, CT, USA.
Biotechnology Research Institute, Kenya Agricultural and Livestock Research Organization, Nairobi, Kikuyu, Kenya.
Parasit Vectors. 2017 Oct 10;10(1):471. doi: 10.1186/s13071-017-2415-y.
Glossina pallidipes is a major vector of both Human and Animal African Trypanosomiasis (HAT and AAT) in Kenya. The disease imposes economic burden on endemic regions in Kenya, including south-western Kenya, which has undergone intense but unsuccessful tsetse fly control measures. We genotyped 387 G. pallidipes flies at 13 microsatellite markers to evaluate levels of temporal genetic variation in two regions that have been subjected to intensive eradication campaigns from the 1960s to the 1980s. One of the regions, Nguruman Escarpment, has been subject to habitat alteration due to human activities, while the other, Ruma National Park, has not. In addition, Nguruman Escarpment is impacted by the movement of grazing animals into the area from neighboring regions during the drought season. We collected our samples from three geographically close sampling sites for each of the two regions. Samples were collected between the years 2003 and 2015, spanning ~96 tsetse fly generations.
We established that allelic richness averaged 3.49 and 3.63, and temporal N estimates averaged 594 in Nguruman Escarpment and 1120 in Ruma National Park. This suggests that genetic diversity is similar to what was found in previous studies of G. pallidipes in Uganda and Kenya, implying that we could not detect a reduction in genetic diversity following the extensive control efforts during the 1960s to the 1980s. However, we did find differences in temporal patterns of genetic variation between the two regions, indicated by clustering analysis, pairwise F, and Fisher's exact tests for changes in allele and genotype frequencies. In Nguruman Escarpment, findings indicated differentiation among samples collected in different years, and evidence of local genetic bottlenecks in two locations previous to 2003, and between 2009 and 2015. In contrast, there was no consistent evidence of differentiation among samples collected in different years, and no evidence of local genetic bottlenecks in Ruma National Park.
Our findings suggest that, despite extensive control measures especially between the 1960s and the 1980s, tsetse flies in these regions persist with levels of genetic diversity similar to that found in populations that did not experience extensive control measures. Our findings also indicate temporal genetic differentiation in Nguruman Escarpment detected at a scale of > 80 generations, and no similar temporal differentiation in Ruma National Park. The different level of temporal differentiation between the two regions indicates that genetic drift is stronger in Nugruman Escarpment, for as-yet unknown reasons, which may include differences in land management. This suggests land management may have an impact on G. pallidipes population genetics, and reinforces the importance of long term monitoring of vector populations in estimates of parameters needed to model and plan effective species-specific control measures.
采采蝇( Glossina pallidipes )是肯尼亚人类和动物非洲锥虫病( HAT 和 AAT )的主要传播媒介。该疾病给肯尼亚的流行地区带来了经济负担,包括西南部地区,该地区经历了强烈但不成功的采采蝇控制措施。我们在 13 个微卫星标记上对 387 只采采蝇进行了基因分型,以评估两个地区在过去 60 年代至 80 年代经历了密集根除运动后的时间遗传变异水平。其中一个地区,Nguruman 悬崖,由于人类活动已经经历了栖息地的改变,而另一个地区,Ruma 国家公园,没有。此外,Nguruman 悬崖在旱季受到来自邻近地区放牧动物进入该地区的影响。我们从两个地区的每个地区的三个地理上接近的采样点收集了样本。这些样本是在 2003 年至 2015 年之间收集的,跨越了大约 96 个采采蝇世代。
我们发现,Nguruman 悬崖的等位基因丰富度平均为 3.49,N 估计值平均为 594,而 Ruma 国家公园的等位基因丰富度平均为 3.63,N 估计值平均为 1120。这表明遗传多样性与之前在乌干达和肯尼亚的采采蝇研究中发现的相似,这意味着我们无法检测到在 60 年代至 80 年代的广泛控制努力之后遗传多样性的减少。然而,我们确实发现了两个地区之间遗传变异时间模式的差异,这表明聚类分析、成对 F 检验和 Fisher 精确检验显示了等位基因和基因型频率的变化。在 Nguruman 悬崖,发现在不同年份收集的样本之间存在分化,并且在 2003 年之前的两个地点和 2009 年至 2015 年之间存在局部遗传瓶颈的证据。相比之下,在 Ruma 国家公园没有发现不同年份收集的样本之间存在一致的分化证据,也没有发现局部遗传瓶颈的证据。
我们的研究结果表明,尽管采取了广泛的控制措施,特别是在 60 年代至 80 年代之间,这些地区的采采蝇仍然存在,遗传多样性水平与未经历广泛控制措施的种群相似。我们的研究结果还表明,在 Nguruman 悬崖检测到了 >80 个世代的时间遗传分化,而在 Ruma 国家公园没有类似的时间分化。两个地区之间时间分化程度的不同表明,Nguruman 悬崖的遗传漂变更强,原因尚不清楚,这可能包括土地管理方面的差异。这表明土地管理可能对采采蝇种群的遗传产生影响,并且加强了对媒介种群进行长期监测的重要性,以估计模型和规划有效物种特异性控制措施所需的参数。