Journal of Threatened
Taxa | www.threatenedtaxa.org | 26 November 2024 | 16(11): 26110–26115
ISSN 0974-7907
(Online) | ISSN 0974-7893 (Print)
https://doi.org/10.11609/jott.7791.16.11.26110-26115
#7791 | Received 24 January 2022 | Final received 03 September 2024 |
Finally accepted 09 November 2024
Diet composition and diet choice
of Lesser Mouse-tailed Bat Rhinopoma hardwickii (Gray, 1831) (Rhinopomatidae:
Chiroptera)
Pawan Kumar Misra
1, Sayma Farheen
2 ,
Shaktivardhan Singh 3 &
Vadamalai Elangovan 4
1,2,3,4 Department of Zoology, Babasaheb
Bhimrao Ambedkar University, Lucknow, Uttar Pradesh 226025, India.
1 pawanmshr17@gmail.com, 2 farheen786stu@gmail.com,
3 shaktivardhansingh@gmail.com,
4 elango70@yahoo.com (corresponding
author)
Editor: H. Raghuram, Sri. S. Ramasamy Naidu Memorial
College (Autonomous), Virudhunagar, India. Date
of publication: 26 November 2024 (online & print)
Citation: Misra, P.K., S. Farheen, S. Singh
& V. Elangovan (2024). Diet
composition and diet choice of Lesser Mouse-tailed Bat Rhinopoma
hardwickii (Gray, 1831)
(Rhinopomatidae: Chiroptera). Journal of Threatened Taxa 16(11):
26110–26115. https://doi.org/10.11609/jott.7791.16.11.26110-26115
Copyright: © Misra et al. 2024. Creative Commons Attribution 4.0
International License. JoTT allows unrestricted use,
reproduction, and distribution of this article in any medium by providing
adequate credit to the author(s) and the source of publication.
Funding: The financial assistance of Science and Engineering Research Board, Department of Science and Technology, New Delhi through a major research project (No. EEQ/2018/000104) to VE is acknowledged.
Competing interests: The authors declare no competing interests.
Ethical statement: Relevant ethical permits were secured for data collection vide Letter No.
214/11/DAAS/BBAU/2011 of Babasaheb Bhimrao Ambedkar University and Archaeological Survey of India, Lucknow circle for bat survey (F. No. 10-16/23/2013-M 11535).
Author details: Pawan Kumar Misra did his PhD on “Isolation and characterization of guanophilic fungi of the bats of Uttar Pradesh” and currently working on educational sector. Sayma Farheen has completed her postgraduation from Babasaheb Bhimrao Ambedkar University and currently pursuing her PhD in Lucknow University, Lucknow, UP. Shaktivardhan Singh has completed his PhD on “Behavioural ecology of the Mouse-tailed Bat, Rhinopoma hardwickii” and currently working on educational sector. Vadamalai Elangovan is professor in the Department of Zoology, Babasaheb Bhimrao Ambedkar University, Lucknow, Uttar Pradesh and working on behavioural ecology of bats since 1996. VE is currently working on “conventional and alternative reproductive strategies of the Indian Flying Fox”.
Author contributions: PKM and SF performed the experimental work, analysed the data and drafted the manuscript. SS supported the field work and data collection. VE designed the experiment and edited the manuscript.
Acknowledgements: The financial assistance of
Science and Engineering Research Board, Department of Science and Technology,
New Delhi through a major research project (No. EEQ/2018/000104) to VE is
acknowledged. We thank the Archaeological Survey of India for permitting us to
conduct the field survey in old monuments of Uttar Pradesh.
Abstract: The food composition and food
choice of R. hardwickii were assessed through
guano analysis at different seasons and geographical locations. Guano samples
of R. hardwickii were collected from the roost
sites of the Gangetic plains and arid region of Uttar Pradesh. Each intact
pellet was dissolved and recognizable insect body parts like legs, antennae,
wings, and mouth parts were separated and photographed. Each insect remnant was
identified to its lowest rank as much as possible. A total of 10 roost sites of
R. hardwickii were observed in the arid region
and Gangetic plains of Uttar Pradesh and all of them were found in historical
monuments. A total of 61 pellets of 10 sites yielded 1,035 remnants of insects.
The highest percentage of remnants belongs to legs, followed by wings,
antennae, abdominal segments, and mouthparts. The remnants belong to eight
insect orders such as Coleoptera, Hemiptera,
Orthoptera, Hymenoptera, Dermaptera, Diptera, Lepidoptera, and Plecoptera.
The remnants of order Hemiptera showed the highest frequency of occurrence
followed by orders Coleoptera, Orthoptera, and
Hymenoptera, and these four orders of insects constitute the major portion of
the diet of R. hardwickii. The orders Dermaptera, Diptera, Lepidoptera,
and Plecoptera contributed a small proportion to the diet of R. hardwickii. The remnants of orders Lepidoptera and Plecoptera were occasional. The result of the current study
shows that the food choice of R. hardwickii
did not differ significantly across roost sites, while differed seasonally. Further,
it reveals that the
Lesser Mouse-tailed Bat acts as a potential and natural insect
balancing agent.
Keywords: Agricultural pest, arid
zone, biological pest controller, guano analysis, insect remnant, insectivorous bat, seasonal food
habit.
Introduction
Bats are voracious in nature and
feed on large scale of insects in a night. Insectivorous bats are the primary
consumers of many nocturnal insects (Kunz & Pierson 1994). They prey on a
variety of agricultural insect pests such as tobacco budworms, corn borers,
plant hoppers, and oriental armyworms (Whitaker 1993). Noctuid moths are major
agricultural pests which are popular for long-distance and seasonal migrations
(Wolf et al. 1990; Westbrook et al. 1995), they are abundantly eaten by bats
(Thompson 1982; Robinson 1990). Insectivorous bats can suppress the pest
population to its lowest level than other known natural enemies (Van Driesche & Bellows 1996). A large colony of
insectivorous bats can deplete the insect pest at large scale; therefore, they
act as potential biological pest control agents (Lee & McCracken 2005).
Several genera of bats including Taphozous, Rhinopoma, Tadarida
and Miniopterus form large
colonies, from few hundreds up to several million individuals (Constantine
1967; McCracken et al. 1994; Elangovan et al. 2018).
The genus Rhinopoma
is monophyletic with only four known species such as R. hardwickii
(Gray, 1831), R. microphyllum (Brünnich, 1792), R. muscatellum
(Thomas, 1903), and R. macinnesi (Hayman,
1937). They preferred to live in groups, forming colonies of hundreds to
thousands of individuals (Elangovan et al.
2018). Very few studies have been
carried out on the diet selection of R. hardwickii.
Feldman et al. (2000) reported that they foraged exclusively in open areas but
did not discuss about diet choice. Advani (1981) reported that R. microphyllum kinneari (Wrougthon, 1912) mainly fed on Coleoptera,
Lepidoptera, and Orthoptera throughout the year, while Isoptera
was the preferred diet during summer and monsoon seasons. No detailed report is
available on diet composition and diet selection of R. hardwickii
at various seasons and habitats in India. Thus, to fulfil the lacuna, a study
on diet composition and diet selection of R. hardwickii
was carried out in arid zones of Bundelkhand and adjoining area of Gangetic
plains in Uttar Pradesh.
Materials
and Methods
Faecal pellets collection and analysis
Field surveys were carried from
April 2019 to February 2020 at arid zones of Bundelkhand (i.e., Hamirpur,
Lalitpur, Jalaun, and Jhansi) and its adjacent
districts of Gangetic plains (i.e., Lucknow and Barabanki)
in Uttar Pradesh. Guano samples were collected from the roost sites by
spreading 2 x 2 m polythene sheet beneath the roost. In addition, the bats were
captured using mist net, each individual was kept in a cotton bag until
defecation, and thereafter they were released at the site of capture. Fresh faecal pellets were collected seasonally, i.e., summer
(March–June), monsoon (July–August), and winter (November–February). Guano samples
were kept in sample vials and stored at -20°C until analysis. Each
intact pellet was soaked and dissolved in distilled water, teased gently using
a fine brush and the insect remnants were separated using forceps. The
recognizable insect body parts like legs, antennae, wings and mouth parts were
separated and photographs were taken under a stereo microscope (RSMr3, Radical
Scientific) using Digital Camera. Each insect remnant was identified to its
lowest rank as much as possible by following Brues et
al. (1954) and online resources. The identified remnants of different sites
were grouped into legs, antennae, wings, and mouth parts and the frequency of
occurrence was obtained.
Statistical analysis
Normality tests were performed to
determine the distribution of the data set (p <0.05), therefore
non-parametric test (Kruskal Wallis H test) was applied to determine the
seasonal and regional variations in the food choice of R. hardwickii. Guidelines of the American Society of
Mammologists for the care and use of mammals were followed (Sikes et al. 2011).
Results
A total of 10 roost sites of R.
hardwickii were observed in the arid region
(Hamirpur, Lalitpur, Jalaun, and Jhansi) and Gangetic
plains (Lucknow and Barabanki) of Uttar Pradesh
(Figure 1). All the roosts of R. hardwickii were
found in historical monuments of the Uttar Pradesh. A total of 61 pellets of 10
roost sites yielded 1035 remnants of insects. The highest proportion of
remnants was legs (47.29%) followed by wings (26.44%), antennae (7.62%), abdominal
segments (5.31%), and mouth parts (0.19%), while the proportion of unidentified
body parts of insects was 13.12%.
The insect remnants belong to
eight insect orders such as Coleoptera, Hemiptera,
Orthoptera, Hymenoptera, Dermaptera, Diptera, Lepidoptera, and Plecoptera.
Further, the valuable diagnostic features of the remnants allowed us to
identify up to family level, e.g., Scarabaeidae, Carabidae and Staphylinidae (Coleoptera), Gryllidae and Gryllicrididae
(Orthoptera), Cynidae (Hemiptera), Formicidae (Hymenoptera). The remnants of order Hemiptera
consist of legs (tarsi with claw; Images 1AH–AI) and wings (hemi-elytra; Images
2L–O). The remnants of order Coleoptera consist of
legs (femur, coxae and tibia, tarsi with claw; Images 1A–V), and wings (elytra;
Images 2A–K), while the order Orthoptera consists of coxae and tibia with claw
(Images 1W–AG) and leathery non–membranous wings (Images 2P–S). Tarsi of Coleoptera were usually heteroamorous and apparently with
three to five segments and one pair of claws (Images 1A–V), while of Hemiptera
with three segments and claw (Images 1AH–AI). The wing remnants of Orthoptera
were membranous, venation rather complete but not complex with pentagonal or
quadrant shape cells (Images 2P–S). They had large legs with spines, tibia with
stout spines and movable spur, tympanum located in front of tibia/rarely
spinose and tarsi with 4–5 segmented claws (Images 1W–AG).
The remnants of Hemiptera showed
the highest frequency in faeces (14.69%) followed by Coleoptera (13.27%), Orthoptera (5.21%), and Hymenoptera
(2.65%). The remnants of orders Dermaptera (0.26%), Diptera (0.17%), Lepidoptera (0.088%), and Plecoptera (0.088%) were found in a small proportion. Further,
a major proportion of insect remnants was unidentifiable (63.53%) because they
were either broken or incomplete. The remnants of orders Lepidoptera and Plecoptera were occasional (Table 1). The remnants
retrieved from faecal pellets showed variation in
diet choice of R. hardwickii at different
localities, i.e., coleopterans were highest in Kakori,
hemipterans in Hamirpur (Maleta), orthopterans in
Jhansi and hymenopterans in Lalitpur (Table 1).
There was no significant difference observed in the occurrence of
remanence of various insect orders in 10 different roost sites, Coleoptera (χ2 = 0.800, p = 0.999), Hemiptera (χ2
= 0.788, p = 0.990), Orthoptera (χ2 = 4.50, p = 0.342), Hymenoptera
(χ2 = 0.330, p = 0.563), Diptera (χ2
= 1.00, p = 0.317), Lepidoptera and Plecoptera (χ2
= 0.00, p = 1.00).
The food choice of R. hardwickii varied with seasons, the remnants of Coleoptera were higher during summer, Hemiptera during
winter, and Orthoptera during monsoon seasons (Table 2). The food choice of R.
hardwickii showed a significant difference during
summer (χ2 = 15.285, p = 0.018), while the food choice did not
differ during monsoon and winter seasons (p >0.05, Table 2).
Discussion
The results of present study
showed that the Lesser Mouse-tailed Bats consumed insects belonging to eight
insect orders across the geographical locations and seasons. The most preferred
food items belong to orders Hemiptera, Coleoptera,
Orthoptera and least preferred items belong to orders Dermaptera,
Diptera, Lepidoptera and Plecoptera.
Feldman et al. (2000) and Whitaker & Yom-Tov (2002) investigated the
habitat utilization and dietary composition of R. hardwickii
and found that they used open habitat and fed coleopteran insects which
contributed about 51% of the diet. Heteropteran (order Hemiptera) insects were
the second most commonly found food items and contributed 30.4% of the diet of R.
hardwickii (Whitaker & Yom-Tov 2002). The
diet selection of many insectivorous bats depends upon dental and cranial
morphology, wing shape, and echolocation call (Neuweiler
2000; Altringham 2011; Weterings
& Umponstira 2014). The results of faecal pellet analysis revealed that the legs and wings
constituted more than 74% of the remnants isolated, while antennae, abdomen,
and mouth parts contributed less than 15%. The highest percentage of legs and
wings in the isolated remnants probably be due to the composition of chitin in
legs and wings.
The Bundelkhand region of Uttar
Pradesh comes under dry-arid zone wherein scarcity of water occurs except rainy
season, while Lucknow and Barabanki are fertile
Gangetic plains. The flora and fauna also vary naturally among the regions; no
difference was observed in the obtained remnants and food choices of R. hardwickii. Although, the food choices vary across
roost sites (geographical regions) but did not differ significantly. The food choice of R. hardwickii
was influenced by seasons. The earlier studies deduced that the prey
availability and prey selection of most insectivorous bats were probably
influenced by temporal, seasonal, and geographical factors (Whitaker 1995;
Whitaker et al. 1996).
Arthropods destroy over 18% of
the annual production of crops worldwide (Culliney
2014). The use of agricultural insecticides causes harmful impact on consumer
and environment. Therefore, use of biocontrol agents for the suppression of
insect pest is very important and the insectivorous bats are good source of
insect pest suppressors as they consume a large number of insects of various
orders. According to Boyles et al. (2013), insectivorous bats decreased the
cost of pesticide about USD 22.9 billion a year and also reduced the
development of pesticide resistance. Similarly, the current study revealed that
the mouse-tailed bats consume a wide range of insects belong to eight orders across
seasons, and geographical areas of Uttar Pradesh. Further, the food choice of R.
hardwickii varies with seasons, and Coleoptera was the most preferred food item in summer,
while Hemiptera and Orthoptera were preferred food items during winter and in
monsoon seasons, respectively. Since, the mouse-tailed bats consume a lot of
insects and play active role as insect suppressor, their roost sites and
populations need adequate conservation for their sustenance and human welfare.
Table 1. The
insect remnants retrieved from faecal pellets of Rhinopoma hardwickii
at different roost locations. The values are given in percentage.
|
Roost locations/ insects order |
Lucknow |
Barabanki |
Lalitpur |
Jalaun |
Jhansi |
Mahoba |
Hamirpur |
|
Coleoptera |
29.55 |
9.09 |
7.58 |
8.33 |
9.85 |
15.91 |
19.70 |
|
Hemiptera |
5.34 |
0.00 |
13.74 |
1.53 |
6.11 |
14.50 |
58.78 |
|
Orthoptera |
7.89 |
2.63 |
13.16 |
10.53 |
39.47 |
7.89 |
18.42 |
|
Hymenoptera |
3.45 |
0.00 |
93.10 |
0.00 |
3.45 |
0.00 |
0.00 |
|
Dermaptera |
33.33 |
0.00 |
33.33 |
0.00 |
33.33 |
0.00 |
0.00 |
|
Diptera |
0.00 |
100.00 |
0.00 |
0.00 |
0.00 |
0.00 |
0.00 |
|
Lepidoptera |
100.00 |
0.00 |
0.00 |
0.00 |
0.00 |
0.00 |
0.00 |
|
Plecoptera |
0.00 |
100.00 |
0.00 |
0.00 |
0.00 |
0.00 |
0.00 |
Table 2.
Seasonal variation in food preference of Rhinopoma
hardwickii. Values are given as Mean ± SD. The
dash (-) indicates the absence of particular insect order during the season.
|
Season |
Summer |
Monsoon |
Winter |
χ2 |
p -value |
|
Coleoptera |
3.70 ± 0.75 |
1.88 ± 0.49 |
2.80 ± 1.94 |
3.42 |
0.18 |
|
Hemiptera |
1.75 ± 0.25 |
2.27 ± 0.798 |
3.58 ± 3.18 |
0.38 |
0.82 |
|
Orthoptera |
0.95 ± 0.08 |
1.22 ± 0.86 |
1.08 ± .12 |
1.293 |
0.52 |
|
Hymenoptera |
- |
7.00 ± 6.00 |
- |
0.50 |
0.48 |
|
Dermaptera |
- |
- |
- |
- |
- |
|
Diptera |
1 |
1 |
1 |
- |
1 |
|
Lepidoptera |
1 |
- |
- |
- |
- |
|
Plecoptera |
- |
- |
- |
- |
- |
|
Unidentified |
8.42 ± 5.45 |
16.1 ± 8.92 |
11.45 ± 4.42 |
1.5 |
0.47 |
|
χ2 |
15.285 |
9.414 |
9.106 |
- |
- |
|
p-value |
0.018 |
0.152 |
0.059 |
- |
- |
For
figure & images – click here for full PDF
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