IntroductionInsectivorous bats constitute about 70% of all bats and are characterized by generally using echolocation to detect prey items (Simmons and Conway, 2003). Nearly all insectfeeding bats are nocturnal (Speakman, 1995), occupy a diversity of habitat types, and exploit a wide variety of prey (Altringham, 1996;Kalko et al., 1996). Some authors have suggested that insect prey abundance influences the local occurrence of insectivorous bats (Rautenbach et al., 1996;Pavey et al., 2001). In other words, changes in the activity level of insects may influence the foraging behavior and activity levels of the bats. Hence, insectivorous bats time their foraging flight patterns to coincide with maximum nocturnal activity of their prey.Abiotic factors such as light, temperature (Russ et al., 2003;Barros et al., 2014), and wind speed (Russo and Jones, 2003;Johnson et al., 2011) exhibit high diurnal fluctuations and are thus likely to influence predator (bats) and prey (insects) activities directly or indirectly. The activity patterns of many nocturnal animals comprise trade-offs between prey availability and predation risk, which are likely to be modulated by light conditions in connection with the lunar cycle. Some studies have shown that moonlight decreases nocturnal activity in animals, including birds (Nelson, 1989), insects (Williams et al., 1956), and rodents (Clarke, 1983). This reduction in activity during periods of high lunar illumination is assumed to hold true for many other bat species (Erkert, 1974(Erkert, , 1978. In addition, Saldaña-Vásquez and Munguía-Rosas (2013) reported that the negative effect of moonlight on tropical bats is higher than on temperate species.According to Findley (1993) and Humphrey (1975), areas that offer a variety of trees and roosts often support the largest numbers of bat species and individuals. In recent years, croplands, plantations, and pastures have significantly expanded globally (Foley et al., 2005). Transformations of land-use types (e.g., forests) via anthropogenic activities are the major drivers behind species loss regionally and globally, through habitat destruction and modification. One such driver that occurs on a global scale is agricultural intensification. This system of farming, which is characterized by high tillage operations, synthetic fertilizers, and pesticide (i.e. agrochemicals) use, is accompanied by loss of