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The call signatures of sixteen Philippine insectivorous bat species are described, and used to inventory bats on Mount Makiling, Luzon. I compare these acoustic diversity data to those collected with mist nets, and a newly designed tunnel trap. The Rhinolophidae used calls with unique constant frequency components. Most vespertilionid calls could be identified to species based on call shape and minimum frequency, with the exception of those used by Pipistrellus spp. and Miniopterus schreibersii. The tunnel trap, mist nets, and the Anabat II detector recorded 22 species, including eight new records for Mount Makiling. Eighteen percent of the species were captured in mist nets, 68% were trapped, and 77% were detected acoustically. Twenty species were recorded either acoustically or with the trap. Two species were recorded exclusively with mist-nets, three with the tunnel trap, and four were only detected with the bat detector. Generally, bats possessing low intensity calls were not detected acoustically or captured in mist nets, but were captured in the tunnel trap. The tunnel trap captured most species flying below the canopy and the bat detector was effective for inventorying those flying above.
This study assesses the extent of midwinter activity (June-July, 1996, 1998) in an island population of lesser short-tailed bat (Mystacina tuberculata) located at the southern limit (= highest latitude) of the species' distribution. Activity of radio-tagged bats (n = 22 bats) was monitored over 38 nights (years combined). A mean ± SE of 64.1 ± 6.5% (range = 0-100%) of radio-tagged bats flew on each night monitored when mean minimum temperature was 3.4 ± 0.5°C. Temperatures ranged from -1.0 to 8.9°C, and 33% of tagged bats flew on the coldest night. Video-monitoring revealed high levels of activity at 11 large communally occupied tree roosts on 100% of nights monitored (n = 31 nights, years combined). Mean minimum temperatures on these nights was 3.0°C ± 0.5 (range = -1.4-7.1). Periods of activity were associated with feeding, social displays and changing roost sites. Movements of bats were dynamic with large numbers emerging from and entering roosts, often simultaneously, throughout most of the night (x = 81.9 ± 3.3% of night). Maximum numbers of active bats in tree cavities at one time numbered > 100 individuals on 75% of nights monitored. These included nine nights when individuals numbered > 500, and five nights when individuals numbered >1,000 (maximum = 1,443). Radio-tagged bats spent 57.1 ± 9.7% of time monitored roosting alone and the remainder roosting communally. They changed roost site on average every 4.2 ± 0.8 days moving between a total of 35 different roosts. Roosts were often re-used either by the same individual or by several different bats. Most radio-tagged bats visited communal night roosts that were different from those they had used during the day, with up to eight radio-tagged individuals visiting simultaneously. Lower levels of activity were recorded at six roosts that were occupied on the same nights as large active communal roosts. Video-monitoring over a total of 31 nights revealed external activity at these roosts on only 11 nights (35.4%). One radio-tagged bat did not emerge for 13 days. 1 suggest that winter activity may not be as energetically expensive for M. tuberculata as for many other cold-temperate bat species. Their ability to forage on terrestrial invertebrates, which are not commonly available to other species, and to select different roost sites where they could either remain active or relatively inactive, may allow them to be active more frequently and for longer durations.
The coefficient of dry mass digestibility (DMD) in the insectivorous bat Myotis myotis (Borkhausen, 1797), fed American cockroaches, is 69.3%. This is comparable with the average digestibility and assimilation coefficients in insectivorous mammals and birds, but it is much lower than estimated in previous studies on Insectivorous bats. The rate of passage of food marked with basic fuchsin (ts = 25, tso = 44, tso = 77 minutes) and the defecation rate indicate extremely rapid digestion of food, which is connected with the feeding and foraging strategies of insectivorous bats. It is con­cluded, that previous estimations of bats' food consumption under natural conditions were lowered by the assumption of high digestibility of food or insignificant amount of feces defecated outside the rest place.
Bat guano supports an assemblage of organisms that varies depending on the species of bat producing it. To determine whether these differences in community structure may be due to differences in guano composition, we analyzed guano from frugivorous (Pteropus rodricensis), sanguivorous (Desmodus rotundus), and insectivorous (Tadarida brasiliensis) bats. We found no differences among species in organic matter or lipid of guano. Desmodus guano contained more carbon (C) than Pteropus guano. The latter contained less nitrogen (N), and the former contained less phosphorous (P) than guano of the other two species. Pteropus guano had a higher C:N ratio, and Desmodus guano had higher N:P and C:P ratios than the other two species. These differences in guano composition suggest that guano from bats in different feeding guilds may affect ecosystem structure and dynamics differently.
Visual flyout count data for the common bent-wing bat Miniopterus schreibersii, collected by a team of observers over two seasons at a disused mine in the Kinglake National Park, south-eastern Australia, was compared with infra-red video footage, collected simultaneously, in order to quantify the precision and accuracy of the observer counts. Bayesian statistical models were used to evaluate the relationship between observer counts and the actual number of bats emerging from the cave, as determined by analysis of the infra-red video footage of the flyout. The accuracy of flyout counts was found to decline with increasing flyout rates, with observers' counts becoming increasingly negatively biased as the rate of bat emergence from the mine increased. In addition, there was evidence of inter-observer variation in the accuracy of the counts. Although the bias in observer counts was relatively small, caution needs to be exercised in interpreting the results of visual flyout counts. We conclude that the use of infra-red video footage for determining numbers is preferable to visual observer counts. The major difficulty in using flyout counts for monitoring is the considerable night-to-night variation in numbers of bats emerging, which could be attributed to variation in the proportion of bats emerging to forage, or to the use of alternative roosting sites by individual bats on successive nights. Both observer error and short-term temporal variation in numbers of emerging bats have the potential to bias population estimates of bats, and need to be properly accounted for if flyout counts are to be used as a tool for population assessment and monitoring.
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