Malaysia is a tropical country that has consistently been facing a prevalent threat of mosquito-borne diseases. Amongst the plethora of diseases, the most common mosquito-borne disease in the country is dengue fever, transmitted by Aedes spp. mosquitoes. This study aims to examine the effects of human activity associated with different land use on mosquito population composition and diversity. Our study site is Chini Lake, a naturally occurring lake and the second-largest freshwater body in Malaysia. The areas surrounding the Lake have been subjected to various human activities, such as economic development and conversion into rubber plantations, while some areas remain pristine, making Chini Lake an ideal location to examine the gradient of human disturbances on mosquito composition and diversity. We sampled adult mosquitoes and larvae across a range of sites with different levels of human disturbance. As expected, in areas with high disturbance scores, the species richness of adult and larval mosquitoes were reduced while the abundance was higher. The results also revealed minimal overlap between species captured for adult and larval samplings, suggesting that land-use changes affect both life stages differently. Different resource requirements of adult and larval mosquitoes likely led to the observed diversity pattern in this small survey. We suggest future work to look into how habitat heterogeneity affects both life stages and sexes of mosquito diversity patterns and distribution.
1. The yellow crazy ant (Anoplolepis gracilipes) is a widespread tropical invasive species that causes ecological damage in introduced habitats; their negative impacts are especially prominent on island ecosystems.2. We examined abiotic and biotic effects on a tropical island (Lang Tengah Island on the East Coast of Malaysia) that experiences annual monsoonal disturbance and hosts two distinct populations of yellow crazy ants.3. To understand how biotic factors affect A. gracilipes, we conducted ant-ant interaction bioassays to examine the extent of aggression levels between populations. 4. We tested the abiotic monsoonal rain effect by employing passive (pitfall traps) and active (quantifying ground foragers on marker crossings) sampling, across pre-and post-monsoon.5. The two populations of A. gracilipes exhibited aggression toward each other. Furthermore, the onset of monsoonal rains reduced A. gracilipes abundance and foraging activity. 6. Our findings suggest that A. gracilipes populations are sensitive to monsoonal rains and long-term population fluctuation data are urgently needed to examine the effect of monsoonal rains on this invasive ant's expansion dynamics on island ecosystems.
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