DOI: https://doi.org/10.21203/rs.3.rs-1585611/v1
The Scotophilus kuhlii inhabits in the various roosts structure including crevices, roofs of abandoned buildings, houses, tree holes. The aim of this study was the seasonal variation in population and how the factors influence of roost selection of S. kuhlii at different seasons as well as different habitats in Uttar Pradesh, India, was done by survey method from 2015 to 2018. Results revealed that the S. kuhlii’s population fluctuates over the season and habitats, which was ranging from one to nine individuals per roost, such as the average roost occupancy was higher in monuments (4.36 ± 2.19 individual) compared abandoned buildings (4.08 ± 2.03) and tree holes (2.64 ± 2.11). Length of roost cavities and roost surface area was crucial factors for roost selection of S. kuhlii, i.e. roost population size is directly proportional to roost surface area and length cavities. Thus, the degree of protection supported the claim that the high protection habitat could yield a maximum roost population size accordingly; the monuments showed a high degree of protection and thus a maximum colony size was observed followed by abandoned buildings and tree holes. In winter S. kuhlii was shifting toward a deeper hole/cavity into roost and in summer toward periphery. We conclude that roost characteristics and roost occupancy influence the roost selection of S. kuhlii.
Roost selection is a subset of habitat selection which influences the survival and fitness of a species. The roost selection of bats is influenced by many factors such as microclimate, structural characteristics of roosts, surrounding habitats, disturbance by humans and risk of predation (Brigham and Fenton 1986; Sedgeley and O’Donnel 1999). Physical characteristics such as the space, shape, thickness of wall and orientation of roost entrance alter the microclimates of roosts and in turn affect the roost quality and roost selection of bats (Kurta 1985; Sedgeley 2001). Further, the shape, size and coverage of entrance and height of the tunnel or roost entrance influence the probability of predation (Medway and Marshall 1972; Vonhof and Barclay 1996; Jenkins et al. 1998). In case of nesting of birds, increase in nest height decreased the predation rate and increased the fitness (Nilsson 1984; Rendell and Robertson 1989; Elliott et al. 1996). Thus, roost quality directly influences the survival and reproductive success of animals, and particularly bats (Li and Martin 1991). Roost plays vital role during reproduction, the female bats of temperate countries form maternity roosts since gestation and leave when the offspring are weaned (Garroway and Broders 2008). Roost offers safe site survival during harsh weather, the bats of temperate zone hibernate in roosts during winter (Kurta 1986) while they aggregate in maternity colonies during breeding seasons (Henshaw 1960; Betts 1997; Entwistle et al. 1997; Williams and Brittingham 1997). A few studies reported that the roosts selected adjacent to water bodies provide food and water (Entwistle et al. 1997; Williams and Brittingham 1997).
Asiatic yellow house bats belong to genus Scotophilus, consist of 15 species worldwide and ranging from Southeast Asia to Africa (Robert et al. 2009). The Asiatic lesser yellow house bat, Scotophilus kuhlii and Asiatic grater yellow house bat, S. heathii roost in monuments, abandoned buildings, fronds of palm tree and tree holes in Uttar Pradesh, India (Rickart et al. 1989; Elangovan et al. 2018). Scotophilus kuhlii readily uses man-made structures as roosts and lives in the roofs of houses, old abandoned buildings (Kingston et al. 2009) and leaf fronds (Rickart et al. 1989). The attics of buildings were used as day roost as well as maternity roost by females of S. kuhlii (Nuratiqah et al. 2017). A few studies had been carried out on seasonal roost selection of tree dwelling bats (e.g. Menzel et al. 2000; Kurta and Rice 2002; Hein et al. 2005; Turbill and Geiser 2008). Although, many studies have been carried out on roost selection of microchiropteran bats (e.g. Sedgeley 2001; Miller et al. 2003; Kalcounis-Riippell et al. 2005; Lacki et al. 2009; Yanzhen et al. 2015), a very few studies been carried out on roost characteristics and roost selection of S. kuhlii (Rickart et al. 1989; Kingston et al. 2009; Nuratiqah et al. 2017).
Bats are facing scarcity of roosts due to various reasons like climatic and anthropogenic changes, and habitat destructions, and thus species like S. kuhlii forced to choose different roost types like monuments, abandoned buildings, other man-made structures, caves, crevices and tree cavities at different seasons. Thus, the aim of this study was to investigate the influence of roost characteristics such as roost height above the ground, tunnel length and width, roost shape, roost surface area, microclimatic conditions and degree of protection of roost at different seasons on roost selection of Asiatic lesser yellow house bat, Scotophilus kuhlii.
The study was carried out between September 2015 to December 2018 in 24 districts of Uttar Pradesh, India. Uttar Pradesh consists of several monuments with distinct styles of architectures of Hindu, Buddhist, and Royal memorials of Indo-Islamic architectures situated in Agra, Banda, Mathura-Vrindavan, Ayodhya, Varanasi, Prayagraj, Kaushambi, Kapilvastu, Kushinagar, Sankisa, Shravasti, Sarnath, Chitrakoot, Lucknow, Jhansi and other small towns.
The roost sites of S. kuhlii were categorized into abandoned building (ruined building not used by human being and not listed as monument by Archaeological Survey of India), monument (historical buildings and palaces protected and listed as monuments by Archaeological Survey of India, Govt. of India) and tree holes (cleft and holes used by bats as roost in large trees like Ficus religiosa, F. virens and F. bengalensis), inthree distinct seasons, these are summer (March–June), Monsoon (July–October) and winter (November–February) (Bhartiy and Elangovan, 2021). The active bat roost was located based on the availability of bat guano on the surface and beneath of the roosts, its pungent odor as well as inquired with local people. Whenever, we found roost, we gave their unique roost ID for second and third observation. Further, we took all measurements of the roost; these are roost height above the ground (m), height of the entrance of roost, width of roost, roost temperature (ºC), humidity (%), and population of roost, types of roost building or trees, length of holes (cm), and roost surface area (m2), length of roost holes or cavity and roost surface areas were measured after emergence of bat because we didn’t disturbed them. Roost height in monuments and abandoned buildings were measured using a measuring tape (m) and tree height was measured using clinometer method. The roost hole or cavity length was measured using a faxable metal ruler (cm). Besides, height (m) and diameter at breast height (dbh, cm) of roost trees were also assessed. Roost temperature and relative humidity were recorded using a Thermo-hygrometer (103-CTH). And also noted the shapes of their inside the roosts structure, which was categorized and naming them as i) ‘T’ shape (both side branched tunnel), ii) ‘┐/┌’ shape (one side branched), iii) unbranched tunnel and iv) crevice or cleft (Fig. 1). Simultaneously, we observed, the roost occupancy of bats, i.e. the bat occupied at periphery of roost or interior part of roost at resting time during day was recorded. We noted the number of individuals in a roost visually and for consistency, gauze nets were placed near the roost entrance at emergence and held until all individuals emerged. Thus we conformed the roost population size. And released them at the site of capture after identification.
Degree of protection (DP) was calculated by using the following formula:
Where T0 was the number of occupied roost observed initially and T1 was the number of abandoned roost observed after 1 year.
The characteristics of unoccupied holes located adjacent to occupied holes were also measured for comparison. The characteristics of unoccupied holes were measured as described above in occupied roosts characteristics. All those parameters of unoccupied holes which showed larger value than the minimum values of occupied holes were considered for comparison.
Generalized liner Mixed Model (GLMM) was used to determine the effect of roost height, tunnel length (holes), roost surface area, roost temperature and humidity and height of roost trees with reference to roost population size of S. kuhlii. The characteristics of occupied roosts and unoccupied roosts, and cavities listed in Table 2 were evaluated using Kruskal Wallis-H test. We also compared the preferred shapes of roosts over seasons listed in Table 3 using Kruskal Wallis-H test. The roost occupancy of S. kuhlii at different seasons was analyzed using Chi-square test. The level of statistical significance considered was p < 0.05. The average values were given as mean ± SD. All statistical analyses were performed using SPSS, ver. 21 and graphs were prepared using Prism Graph-Pad version-5.00.
The roosts of Scotophilus kuhlii were often observed in monuments, abandoned buildings and trees holes. On two occasions, the colonies of S. kuhlii were observed in palm fronds with more than a hundred individuals, in the whole study period. They used naturally existing holes in the walls of monuments and abandoned buildings as well as in the clefts of larger trees in various places of Uttar Pradesh, India. A total of 192 roosts were found, and consist 702 (sum of the whole roost's population) population of S. kuhlii were observed from September 2015 to December 2018 in 24 districts of Uttar Pradesh, India (Fig. 1). The population size was fluctuated over the seasons and type of roosts and which was ranged from one to nine individuals per roost. A maximum percentage of roosts were observed in an abandoned building (N = 90, 46.87%) followed by monuments (N = 78. 40.7%) and tree holes (N = 25, 13.02%), while the highest number of individuals were observed in monument’s roost (323 individuals) followed by abandoned buildings roost (305 individuals) and tree holes (74 individuals). Akin to the number of individuals in each roost type, the average roost occupancy was higher in monuments (4.36 ± 2.19n) than abandoned buildings (4.08 ± 2.03n) and tree holes (2.64 ± 2.11n), and the roost occupancy varied significantly among roost types (χ2 = 99.47, p < 0.05) with seasons. Whereas, the highest level of protection was observed in monuments (96.29%) followed by abandoned buildings (78.50%) and tree holes (60%, Fig. 6). Scotophilus kuhlii preferred to roost at different heights across roost types and seasons (Fig. 3b). As a result, their roost population size varied among roosting sites (Monuments, Abandoned buildings and trees) with seasons (Fig.. 3 a).
The highest roost` height was observed in trees (4.68 ± 1.32m) followed by abandoned buildings (4.36 ± 1.42m) and monuments (4.06 ± 1.59m). Statistical analysis has shown the least positive fixed coefficient (µs 0.001) between the roost height and roosts population size, which has been varied by seasons and roost types (GLMM, F = 0.989, p = 0.321) (Table 1). The highest roost holes length was observed in monuments (19.28 ± 8.49cm) followed by abandoned buildings (16.77 ± 10.95cm) and tree holes (16.08 ± 8.01cm), whereas statistically analysis has been shown significantly different with season and habitats ( GLMM, F = 65.01,p = 0.0001) in (Fig. 3c). Besides, these are showed a positive coefficient between the length of the roost holes and the corresponding population size (Table 1).
The roost surface areas were varied with the length of the roost holes, which was selected by S. kuhlii at different seasons (Fig. 3d). While there was the highest roost surface area was observed in monuments (2.88 ± 1.73 m2), followed by abandoned buildings (2.55 ± 1.71m2) and tree holes (2.16 ± 1.60 m2), which was showing highly positive coefficient significant with population size (GLMM, F = 29.276,p = 0.0001). The bats were chosen highest roost area in monuments and trees during summer and the least roost area during winter (Table 1). As a region Scotophilus kuhlii chosen various shapes of roost structures, these are following roost shape, was often seen such as a ' 'T' shaped roosts (50.5%) followed by '┐/┌' shaped (36.4%), un-branched tunnel (7.2%) and crevice or cleft (5.7%). It has shown statistical significance among the shape of roost (H = 60.466, df = 3, p = 0.0001). As a result shape of the roost effect on the season has been shown significantly different (H = 9.188, df = 2, p = 0.010). However, there was no significant effect of roost shapes between population size of S. kuhlii (p > 0.05; Table 2), except in crevice roosts (H = 6.70, p < 0.05) shown high preference during summer.
Besides, the position of roost occupancy by S. kuhlii was varied over seasons, they were occupying the periphery region inside the roost’s holes or cavities (3.00 ± 2.03cm) in summer followed by moderate interior (3.93 ± 2.08cm) in monsoon, and deep interior (5.33 ± 3.78cm) in winter. The average ambient temperature was recorded in summer (36.38 ± 7.51 oC) followed by monsoon (31.56 ± 2.73 oC) and in winter (17.53 ± 6.22 oC). It was negative coefficient effect on population size (GLMM, F = 11.332, p = 0.0001) (Table 1). While roost temperature was varied over the seasons (Fig.. 3e), which the temperature fluctuation was occurring the least variation was recorded in monsoon among the habitats except in summer and winter. These are in monuments (32.82 ± 5.30oC) and abandoned buildings (31.40 ± 3.048oC) and tree holes (36.15 ± 2.54 oC) and (18.77 ± 6.34oC), (28.82 ± 7.30oC) and in trees (18.31 ± 8.34oC) respectively (Fig. 3e). As a result, the roost temperature has shown a significant impact on the root’s selection in seasons (GLMM, F = 29.276, p = 0.0001) (Table 1). The relative humidity was ranging from 90.3–64.2% (Fig. 3f). A maximum humidity was recorded in tree holes (90.31 ± 1.1%) followed by monuments (84.03 ± 14.0%) and abandoned buildings (80.72 ± 6.9%). There was no effect of humidity on the roost population size of S. kuhlii,(GLMM, F = 0.375,p = 0.541), but has been shown a positive coefficient with population size. (Table 1).
Roost height above the ground and length of the roost holes were higher in occupied roosts compared to unoccupied holes available at abandoned buildings and monuments (Fig. 4a-b). The height of the occupied roost entrance was shorter in both abandoned buildings and monuments than in the unoccupied tunnels (Fig. 4d). The roost height above ground, length of roost holes and height of holes entrance showed a significant difference (p < 0.001) (Table 1). The widths of occupied roost entrance abandoned buildings and monuments were similar to unoccupied tunnels and did not show a significant difference (p > 0.05) (Fig. 4c 4). The height of roost and non-roost trees was almost the same and there was no significant difference among them (p > 0.05) ( Table 1,) but the DBH of occupied roost trees was higher than non-roost trees (Fig. 5 ) and differed significantly (p < 0.001).
The water source was universally accessible to all roosts. The roosts were within (2.22 ± 1.83km2) in summer, followed by (2.05 ± 1.83km2) in monsoon and (1.76 ± 1.50km2) in winter. Thus foraging ree sources such as open ground, garbage site clustered trees, the roosts were within (0.77 ± 0.16km2) in summer (0.15 ± 0.1km2) in monsoon and (0.3 ± 0.25km2) in winter.
The examination of these data supports the contention that selection of the roost by S. kuhlii and its population was varies throughout the seasons among the habitats in Uttar Pradesh, India shows its wide distribution in the region. S. Kuhli was often observed to have a normally distributed average number of bats in a roost, with observed roost population sizes ranging from one to nine individuals per roost throughout the season, and of the roost type, resulting in the population of this species being healthy. As a result roost population depends on the space inside the roost, in the habitats like man-made structure as well as cavities in trees. While in the present study also found occasionally large numbers of S. kuhli in a palm tree with more than about three hundred individuals per roost. Earlier study has also reported that the colony size of S. kuhlii could be from a few individuals to several hundred (Smith and Xie 2008).
The cavities of roost in manmade structures, as well as trees, were playing a significant role in roost selection with the season. As a result, abandoned buildings and monuments offered more abandoned cavities or holes which was often occupied by S. kuhlii (Bhartiy and Elangovan 2020), moreover the monuments were more inhabited by S. kuhlii due to often less predator's effect was observed such as cat, snake and some other vertebrates predators etc. because this is a protected place that comes under the Archaeological Survey of India. The degree of protection supported the claim that the high protection habitat could yield a maximum population size; accordingly, the monuments showed a high degree of protection and thus a maximum colony size was observed followed by abandoned buildings and tree holes. The selection of high-quality roosts influences on survival and fitness of bats while a poor-quality roost invites predation. Consistently, Monuments provide a stable climate and higher protection from predation throughout the year even in adverse conditions. This could be the reason S. kuhlii preferred monuments for roosting over an abandoned building and tree holes. Trees provided the least level of protection and possibly stable climatic conditions compared to monuments and abandoned buildings. In unfavorable conditions like heavy rain or low ambient temperatures, found warm and dry conditions in the monument and abandoned building roost which is suitable for the healthy population of S. kuhlii, but did not found in trees like this. So buildings roost may play a crucial role during the critical life stages such as reproduction. Likewise many species of bats such as Megaderma lyra (Subbaraj and Balasingh 1986), Nycteris grandis (Fenton et al. 1990), Nyctalusleisleri (Shiel and Fairly 1999) and Antrozous pallidus (Lewis 1994), greater sac-winged bat, Saccopteryx bilineata (Bradbury and Emmons 1974; Bradbury and Vehrencamp 1976), greater mouse-eared bat, Myotis myotis (Dietz et al. 2009), spear-nosed bat, Phyllostomus hastatus (Santos et al. 2003), and free-tailed bats such as Tadarida brasiliensis and Mops condylurus (Vivier and van der Merwe 2001) use building as a shelter for roosting. Kurta (1992) reported that building-roosting bats gave birth earlier than their conspecifics roosting in foliage or trees that are the advantage of building-dwelling roost over tress dwelling roost. However, an earlier report suggested that on roosting ecology of S. kuhlii, modify the fronds of a fan palm, Livistona rotundifolia as tent roost and live (Rickart et al. 1989). Whereas trees provide the very least stable temperature, humidity and protection from the predators, therefore the selection of tree roosts was less compared to monuments and abandoned buildings.
Although the height of the roosts did not matter for the selection of roosts between habitats with the seasons, their roosts were often found at moderate heights, creating healthy roosts with colony sizes ranging from a meter to four meters. Speculation that moderate elevation assorted with resting places of other animals; these can be birds' nests as well as abandoned holes or cavities, resulting in a lack of precise detection of prey by predators. If high and low roosts can offer more predators, then high altitude roosts can be easily visible but low altitude roost predators can easily reach their roost, which is a life threat for bat survival. While few studies have been reported that high roosts also offer bats greater protection from predators (Rydell et al. 1996; Vonhof and Barclay 1996). Another reason may also play a crucial role in roost selection because Scotophilus kuhlii is a low flier which could be a possible reason for the preference of roosts at medium height. The cavity lengths of all roost types and across the seasons were positively correlated with population size which shows a significant role in roost selection. The length of cavities was varied among roost types and associated with protection. Further, the larger size of cavity length was providing more space to S. kuhlii for roosting. As a result, increasing the surface area of roosts. And varied among roost types and determined the fitness, i.e. roost occupancy. Therefore, perhaps the roost surface area was positively correlated with the population size. Previous studies report that the roost area may be an important factor in maintaining a healthy colony that helps in thermal maintenance during hibernation by social clustering (Veilleux and Veilleux 2004). The social organization directly depends upon space inside roosts used by bats, which limits the number and their ability to cluster together (Kunz 1982). Willis et al. (2006) reported that female big brown bats (Eptesicus fuscus) preferring roost with larger cavities and cavity volume was positively correlated with roosting-group size.
The shapes of roosts played a key role in the roost selection of S. kuhlii as the shape of roosts was associated with the protection level. Out of total roosts observed, the most preferred was 'T' shaped roost followed by '┐/┌' shaped, unbranched tunnel and crevice. The area of 'T' shaped roost was always higher than '┐/┌' shaped, unbranched tunnels and crevice, and thus the preference of 'T' shaped roost was higher than other types of the roost. During the study period, it was often observed that in "T" and "L"-shaped roosts, whenever, an attempt was made to catch them (S. kuhli), they migrated to other sites inside the roost. Besides, it played an important role in the breeding season, the roots thus becoming the maternity roosts. Because the puppies used to hide inside such a place in the absence of the mother. While nature like this, rare was found in another roost such as in un-branch holes and crevices.
The shape and size of roost directly affect the microclimate of roost (Entwistle et al. 1997; Vonhof and Barclay 1997; Williams and Brittingham 1997), which is directly related to the survival of bats and the developments of their offspring (Racey and Swift 1981; McNab 1982). There was no significant difference in the shapes of roost among three different seasons which shows the highest preference to 'T' shaped roosts showing significant differences among the shapes of the roosts with habitats.
The humidity of roosts was varied according to the seasons but did not matter on roosts selection of S. kuhlii, perhaps so there was no significant difference among the seasons except summer have the least humidity of the roosts. Previous studies have been shown that stable microclimates such as humidity and temperature would help lower the metabolic rate and energy expenditure of bats (Usman 1988). For successful reproduction, water, as well as energy, is an important factor (Kurta et al. 1990) and in small bats, water balance is very sensitive to temperature and humidity (Herreid and Schmidt-Nielson 1966). So many authors reported that bat roosts such as maternity roost, hibernacula roost with high humidity (Twente 1955; Herreid 1963; Clawson 1979; Van Der Merwe. 1987; Churchill. 1991; Baudinette et al. 1994; Clark et al. 1996; Betts 1997). High humidity reduces evaporative heat loss (Bakken and Kunz 1988; Webb 1995) and prevents dehydration (Vander Merwe 1973). Webb et al. (1995) also reported that the high ambient temperatures and RHs would tend to slow down the evaporative water loss of active bats. The warm and stable temperature of maternity roosts allows breeding females to reduce their energy expenditure that remains them active and homeothermic for a longer period. Previous studied reports that S. kuhlii selecting roosts with almost high and stable humidity and temperature without much change within the seasons (Shek and Chan 2006). Harbusch and Racey (2006) reported that buildings offered suitable temperatures during gestation and lactation periods that are critical for the survival of their offspring.
The present study showed that roost temperature was always slightly cooler than the ambient temperature in summer and warmer in winter, as a result taking advantage of the energetic saving during hibernation. Warmer of roost means lower the metabolic rate and increased rate of gestation, postnatal growth and long survival rate (Racey 1982; Kunz 1987; Zahn 1999). And also crucial factors for survival in winter, to low investments of energy, as a result, cooler roost needs more energy to warm compared to worm roost. Therefore, colonies of S. kuhlii were often maintained roost warm temperature and lower metabolic rate through the position of roost occupancy such as anterior and posterior. During summer and monsoon, it was occupied on the peripheral position of roost and in winter it was a shift to the interior position of the roost in monuments and abandoned buildings and the tree cavities. It was seen the roost sifting is a common of S. kuhlii over the season and adverse condition. In winter S.kuhlii sifting in a deeper hole/cavity into roost and in summer income out on the periphery.
The distinct characteristics between occupied roosts and unoccupied tunnels available adjacent to the occupied roost showed that S. kuhlii selects its roost wisely as the roosts influence survival and fitness. This study revealed that the factors such as roost cavity length and shape, roost surface area, roost height and associated protection influence the roost selection of S. kuhlii. The outcome of this study could be useful to understand the life history and future conservation of S. kuhlii. The roost height above the ground, tunnel length and height of roost entrance differed significantly between occupied roost and available unoccupied tunnels. However, the tunnel width did not differ significantly between occupied roost and unoccupied tunnel. It shows that the roost selection in S. kuhlii is influenced by various factors. Barclay et al. (1988) reported that roost of small to medium-sized entrances may provide better insulation and protect the interior from extremes of weather. Although, several studies have shown that several bat species (Tidemann and Flavel 1987) and other cavity dwellers (McComb and Noble 1981) uses cavities with entrance holes not much larger than themselves, thus excluding larger predators and competitors. In this study, the selection of roost by S. kuhlii was not random among available cavities. There were differences in roost height above the ground, length of the tunnel, the width of the entrance, the height of roost trees and dbh of occupied roost and unoccupied roost. The degree of protection plays a critical role in roost selection. The results showed that the degree of protection was driven principally by tunnel lengths, the shape of roosts and optimum roost height at different roost habitats. The degree of protection was highest in monuments followed by abandoned buildings and tree holes. A maximum number of individuals of S. kuhlii were found roosting in monuments followed by abandoned buildings and trees.
Acknowledgements
We thank Dr. B. Lal and Dr. Poonam, Remote Sensing Application Centre, Lucknow, Uttar Pradesh, India for their support in preparing map of study area and Archaeological Survey of India for permitting us to conduct the field survey in old monuments of Uttar Pradesh.
Author contributions: SKB performed the experimental work and data analysis and drafted the manuscript. VE designed the experiment and edited the manuscript
Funding: The authors have no relevant financial.
Conflict of interest: The Authors declare no conflict of interest.
Ethical approval: Not applicable.
Consent to participate: All authors have approved the current contents of the manuscript and its submission to Biodiversity and Conservation.
Consent for publication: All authors have approved the current contents of the manuscript and its submission to Biodiversity and Conservation.
Table 1. The effect of roost characteristics of different roost types on population size of S. kuhlii at different seasons are given in parentheses (GLMM values). The values of roost characteristics are given as mean ± SD.
Variable |
Mean ± SD |
t |
p |
||
Summer |
Monsoon |
Winter |
|||
Roost height above the ground (cm) |
4.09 ± 1.21 |
4.11 ± 1.55 |
4.015 ± 1.340 |
0.995 |
0.321 |
Length of hole (cm) |
19.28 ± 8.49 |
16.77 ±10.95 |
16.086 ± 8.013 |
8.127 |
0.0001 |
Height of entrance (cm) |
7.99 ± 2.91 |
7.53 ± 2.643 |
6.748 ± 2.765 |
1.578 |
0.116 |
Width of entrance (cm) |
8.88 ± 3.26 |
9.27 ± 3.052 |
9.889 ± 4.193 |
-3.832 |
0.0001 |
Ambient Temp (ºC) |
35.38 ± 7.51 |
30.56 ± 2.730 |
17.536 ± 6.223 |
-3.461 |
0.001 |
Roost temp (ºC) |
32.82 ± 5.30 |
31.407 ± 3.040 |
18.778 ± 6.340 |
3.65 |
0.0001 |
Humidity (%) |
47.73 ± 23.94 |
75.817 ± 23.236 |
74.882 ± 11.610 |
0.666 |
0.506 |
Roost area m2 |
2.885 ± 1.731 |
2.163 ±1.604 |
2.554 ±1.717 |
5.368 |
0.0001 |
Distance from adjacent water source (km) |
2.22 ± 1.83 |
2.054 ± 1.216 |
1.761 ± 1.501 |
-0.462 |
0.645 |
Distance from feeding ground (km) |
0.77 ± 0.16 |
0.157 ± 0.10 |
0.301 ± 0.255 |
1.674 |
0.096 |
Table 2. Selection of different roost shapes at different seasons and their effects on colony size of Scotophilus kuhlii. Values are given as mean ± SD.
Season / Shape of roost |
T-shaped |
┐/┌-shaped |
Unbranched tunnel |
Crevice |
Summer |
4.64 ± 20 |
3.57 ± 2.17 |
2.64 ± 1.78 |
4.71 ± 1.79 |
Monsoon |
4.70 ± 2.39 |
3.07 ± 2.03 |
2.50 ± 1.77 |
1.00 ±0. 00 |
Winter |
4.21 ± 2.02 |
3.78 ± 2.27 |
3.00 ± 1.00 |
2.00 ± 0.00 |
*H |
2.508 |
3.91 |
0.540 |
6.70 |
P |
0.285 |
0.141 |
0.763 |
0.034 |