Bawean warty pig and Bawean deer 895
TABLE 1 Species that were detected during a 13-month camera–trap survey on Bawean Island (Fig. 1a), with their IUCN Red List status, regional status, total relative abundance index (RAI), mean RAI, number of video records, number of camera-trap days until first detection, and per cent of total records.
Species
Mammals Bawean deer Axis kuhlii
Sunda porcupine Hystrix javanica
Long-tailed macaque Macaca fascicularis
Common palm civet Paradoxurus hermaphroditus
Bawean warty pig Sus verrucosus blouchi
Reptile Common water monitor Varanus salvator
Birds Purple heron Ardea purpurea
Emerald dove Chalcophaps indica
Green junglefowl Gallus varius
Red List category1
CR LC LC LC EN
LC
LC LC LC
Regional status
Protected Protected
Not protected
Not protected
Not protected
Not protected
Not protected
Not protected
Not protected
Total RAI2
0.84 0.07
38.35 0.16
21.81 0.13
0.04 0.02 0.11
Mean RAI ± SD3
0.46 ± 2.44 0.09 ± 1.09
No. of videos
38 3
29.68 ± 34.12 1731 0.07 ± 0.49
7 15.77 ± 23.42 985 0.12 ± 1.11
0.16 ± 2.15 0.01 ± 0.19 0.04 ± 0.56
6
2 1 5
Camera-trap days until first detection
507 265 115
1188 49
526 595
3928 1722
% of total records
1.4 0.1
62.3 0.3
35.5 0.2
0.1 0.0 0.2
1CR, Critically Endangered; EN, Endangered; LC, Least Concern. 2All detections for a species summed for all camera traps over all days, multiplied by 100 and divided by the total number of camera-trap nights. 3Mean of the RAI of each camera trap.
(dusk), noon and midnight. We used a χ2 test to compare the frequency of observations between sunset and sunrise and between sunrise and sunset, the timings of which were obtained from the Astronomical Applications Department of the U.S. Naval Observatory.
Results
Relative encounter rates, distribution and habitat preferences
In total we accumulated 4,516 camera-trap days, with 2,278 independent videos of ninewildlife species (Table 1). Domes- tic species recorded were water buffaloes (2 videos), feral dogs (44), cats (14) and chickens (3). In addition, there were 28 videos of unidentified species of rats.We could not detect any significant difference in the relative abundance index be- tweenwet and dry seasons for either of the focal species (deer: RAI wet = 0.57, RAI dry = 0.38;W= 3,619.5,P = 0.498; warty pig: RAI wet = 16.51,RAI dry = 15.21;W= 3,427,P = 0.367). Baweanwarty pigs were present in the three largest forest
blocks but absent from the two smallest fragments and the western peninsula Gili Barat (Fig. 1b). Given the sensitivity of the data, we refrain from publishing distribution data for the Bawean deer. However, 90% of all videos were recorded
in a single area of c. 17 ha, with 29 videos recorded from only two camera traps. In all of these locations, camera traps also recorded feral dogs. Fifty-five camera-trap locations were excluded from oc-
cupancy analysis of the Bawean warty pig because of missing covariate information. Of the remaining 126 sites, Bawean warty pigs were detected at 59, giving a naïve occupancy of 0.47. The top-ranking model indicated only a negative influence of distance to nearest village on probability of
occupancy (−0.56 ± SD 0.24; Fig. 2).Moonlight, temperature and rainfall did not significantly influence detection prob- ability and all other site-level covariates for probability of occupancy were similarly unable to improve model fit, such that there were no competing models (ΔAIC,2). The revised model-derived estimate of occupancy for the Bawean warty pig was 0.59 ± SD 0.06, with a detection probability of 0.17.
Population size
Random encounter modelling based on the four trapping periods yielded variable population estimates for the Bawean warty pig, ranging from a minimum of 75 individuals in October and November to a maximum of 2,219 in June and July (Table 2). Our overall mean estimate across the entire study period is 351 mature individuals.
Oryx, 2020, 54(6), 892–900 © 2019 Fauna & Flora International doi:10.1017/S0030605318000996
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