Journal of Threatened
Taxa | www.threatenedtaxa.org | 26 April 2025 | 17(4): 26763–26779
ISSN 0974-7907 (Online) | ISSN 0974-7893 (Print)
https://doi.org/10.11609/jott.9494.17.4.26763-26779
#9494 | Received 16 November 2024 | Final received 24 February 2025 |
Finally accepted 18 March 2025
Biodiversity in Garh Panchkot and
surroundings (Purulia, West Bengal) of residential and migratory land
vertebrates with special reference to endangered species
Amrita Panja 1, Biplab
Kahar 2 & Sujoy Chattaraj
3
1,2,3 Panchakot Mahavidyalaya, Neturia,
Sarbari, Purulia, West Bengal 723121, India.
1 amritapanja87@gmail.com
(corresponding author), 2 biplab.kahar1984@gmail.com, 3 sujoychattaraj2002@gmail.com
Editor: Jayanta Kumar Mallick, Wildlife Wing,
Kolkata, India. Date of publication: 26 April 2025
(online & print)
Citation: Panja,
A., B. Kahar & S. Chattaraj (2025). Biodiversity in Garh Panchkot and
surroundings (Purulia, West Bengal) of residential and migratory land
vertebrates with special reference to endangered species. Journal of Threatened Taxa 17(4): 26763–26779. https://doi.org/10.11609/jott.9494.17.4.26763-26779
Copyright: © Panja et al. 2025. 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:
None.
Competing interests:
The authors declare no competing interests.
Data availability statement: The
original contributions presented in the study are included in the
article/Supplementary Material; further inquiries can be directed to the
corresponding author.
Author details: Dr. Amrita Panja: AP is currently
appointed as assistant professor (stage-I), in Department of Zoology, Panchakot
Mahavidyalaya, Purulia. She has completed her M.Sc
(Zoology) with specialization in molecular biology and human genetics and
gained more than 12 years of research experience. Her main area of interests is
molecular biology, cytogenetics, biotechnology, and ecology-biodiversity. Dr. Biplab Kahar: BK is a veteran
Zoologist and academician, serving Panchakot Mahavidyalaya, Purulia in the
capacity of an assistant proffesor (stage-II) and HOD Department of Zoology. He
has more than 10 years of teaching experience to his credit at undergraduate
level. He has presented research papers in various International and national
seminars. Mr. Sujoy Chattoraj: SC
has completed M.Sc with specialization in fishery. He
is at present designated as SACT-II in Department of Zoology, Panchakot
Mahavidyalaya, Purulia. His areas of teaching interests include fishery,
development biology, ecology and functional anatomy of chordates and
non-chordates.
Author contributions: AP
wrote and conceptualised the manuscript. BK coordinated and analysed the data.
SC captured the wild life photographs and organise the sample information. All
authors contributed equally to the article and approved the submitted version.
Acknowledgements: The authors express their gratitude
to the local tribal hunters and residents of the nearby villages in the Garh
Panchkot hilly region for sharing valuable information that contributed to the
study of biodiversity among land vertebrates in Garh Panchkot and its
surrounding areas, Purulia, West Bengal, with a particular focus on endangered
species.
Abstract: This study examined land
vertebrate biodiversity in Garh Panchkot (Panchet Hill) and surrounding forest
areas in Purulia, West Bengal. Opportunistic field surveys and direct specimen
collection were used to assess the abundance of endangered and vulnerable
species. Previous studies recorded 106 land vertebrate species in the region,
with the highest diversity in the class Aves and the lowest abundance in the
class Amphibia. Endangered species recorded in the current study included
Peafowl Pavo cristatus, Sloth Bear Melursus ursinus, Common
Langur Semnopithecus entellus, Rhesus Macaque Macaca mulatta,
Indian Rock Python Python molurus, and Fishing cat Prionailurus
viverrinus. Also observed were Black-headed Ibis Threskiornis
melanocephalus and Striped Hyaena Hyaena hyaena classed as “Near
Threatened,” and White-rumped Vulture Gyps bengalensis designated
“Critically Endangered”. An analysis of likely threats to vulnerable species
identified rapid urbanization, accompanied by increased air, water and noise
pollution. The results of this study will be useful in establishing
spatiotemporal distribution patterns of land vertebrates and especially
threatened species, aiding efforts to promote bio-conservation and sustainable
development.
Keywords: Bio-conservation, diversity,
endangered species, land vertebrates, Panchet Hill, Purulia, spatiotemporal
distribution, threats, vulnerable species.
INTRODUCTION
In the modern era, global
biodiversity is progressively exhausted at a higher rate. Biodiversity has
vital ecological role in maintaining the stability and support all forms of
life within ecosystems. The term biodiversity loss,
describes the reduction in genetic variability, biological diversity, and the
natural ecosystem organizations (Sanyal et al. 2012; Achieng et al. 2023).
India is regarded as one of the world’s most varied nations, home to
approximately 7–8 % of all known species as well as a few hotspots with diverse
ecosystems, enhanced biodiversity (Himalaya, Indo-Burma, Western Ghats,
Sundarbans) and it serves as a huge archive for traditional knowledge. Based on
nationwide survey, it has been estimated that there are around 69 endemic bird
species, 156 reptile species, and 110 endemic amphibian species in India (UNEP
2001; Rana & Kumar 2023). The recorded percentage of forest area in West
Bengal is 13.38% (11,879 km2) of the geographical area (88,752 km2),
whereas the corresponding data for Purulia District is 14% (Northern tropical
dry deciduous forests cover an area of 876 km², which includes 112 km² of
reserve forests, 729 km² of protected forests, and 35 km² of unclassed state
forests and other areas) of the geographical area (6,259 km2)
(Annual Forest Administrative Report, West Bengal, 2021–2022). There are around
eight different kinds of woods, each with a diverse range of vegetation and
fauna. West Bengal’s rich biodiversity combines the elements of the Himalayan,
sub-Himalayan, and Gangetic plains in its diversified flora and wildlife. Garh
Panchkot, a ruined fort, which dates back to probably the 90 AD is situated
right by the Panchet Lake along the foothills of the famous Panchet Hill. This lush dense forested area was once
fortified. Panchet Hill (Garh Panchkot) is located at the lateritic landscape
of the Neturia Community development Block under the Raghunathpur subdivision
of the Purulia District (northeastern tip of Purulia) and it has a maximum
elevation of 650 m.
Garh Panchkot is rich in
biological diversity. The inventories of flora in the sample plots include 40
tree species, 15 shrub species, seven liana species, and 18 herb species
(https://westbengalforest.gov.in). Garh Panchkot also harbours 325 medicinal
plants having rich gene pools of many threatened species. The lovely chirping
and symphony of several bird species fill this remote, calm, and serene valley.
In addition to the breathtaking beauty of nature, Garh Panchkot is renowned for
its rich zoological treasure and a testament to a rich historical past. An
assessment of the variety of bird species in and around Purulia Town, West
Bengal, India, was conducted by Mahato et al. (2021). Mandal (2012) performed
another investigation that identified uncommon macrophyte species connected to
wetlands in the Purulia Districts. Raha & Pandey (2015) studied the
hunting festival which causes a serious threat to the biodiversity of Ajodhya
Hills, Purulia. Moreover, Samanta et al. (2017) and Das (2018) investigated on
the butterfly diversity of Purulia, especially in the Baghmundi Region. Another
study on diverse butterfly species and related host plants in Joychandi Hill of
Purulia District, West Bengal was carried out by Chowdhury & Chowdhury
(2020). Previously, a field study was performed on butterfly diversity in
correlation to habitat utilization in Purulia (Das 2018). In addition, few more
studies were done surrounding the Bagmundi Hill and Garh Panchkot area upon
insect diversity (Sengupta et al. 2021; Mukherjee & Hossain 2024). Bhowmik
et al. (2017) studied on snake biodiversity in Garh Panchakot and its
surrounding areas in Purulia District. Another documentation was done by
Samanta et al. (2021) on the globally threatened Indian Pangolin and its
threats from Ajodhya Hills of Purulia. Sikdar et al. (2024) observed the
coexistence of Indian Pangolin Manis crassicaudata (Mammalia: Pholidota:
Manidae) and Indian Crested Porcupine Hystrix indica (Mammalia:
Rodentia: Hystricidae) in Purulia District. Garh Panchkot, Purulia has been
least explored regarding the threatened land vertebrate diversity and
comparatively little published information is available to date. At present,
there are scanty reports available on the prevalence of endangered faunal
species in the Purulia District’s Garh Panchkot region. The goal of the current
field work is to gather up-to-date information about the land vertebrate
species with special emphasis on the variety of Near Threatened (NT),
Vulnerable (VU), Endangered (EN), and Critically Endangered (CR) in the Panchet
Hill and adjoining forest areas. Investigating species abundance, likely causes
of threats and extinction, and potential management approaches to save
endangered species are the further objectives of the present study.
MATERIALS AND METHODS
Study area
The Purulia District is primarily
associated with West Bengal’s Chotanagpur Plateau. The district experiences
subtropical weather, with summer temperatures reaching as high as 400C
and winter lows of 70C with average rainfall 1,375.2 mm. The area is
made up of highlands, low hills, scenery, and dense Sal Forest 0.61%, mixed
dense forest 2.27%, open Sal Forest 1.80%, mixed open forest 12.20%, other
social forestry plantations and degraded forests (https://purulia.gov.in). The
majority of the rainfall runs off due to the topography’s undulations. The
hilly location of Garh Panchkot (23.6 0N & 86.7 0E)
has been the primary focus of this investigation (Image 1). This study area is
60 km away from Purulia Town and is part of the Neturia Block. Nine villages
surrounding the Panchet Hill (Bagmara, Puapur and Chalmara villages are
situated at the northern side whereas Panchut and Gobag at the southern side;
Rampur, Lakhmanpur, and Aamdanga on the western side of the hilly region) were
selected during the study as the focal sites. The aforementioned villages
surrounding the Panchet Hill were included in this study as these are the
habitats of several vertebrate species, including Jungle Cat, Indian Flying
Fox, House Rat, Bengal Fox, Indian Grey Mongoose, Common/Brahminy Skink,
Oriental Garden Lizard and birds such as Kingfisher, Asian Openbill, Dove,
Parakeet, Red-naped and Black-headed Ibis. The area is also home to endemic
species, including Indian Pangolin, Indian Crested Porcupine, and Striped
Hyena. For the detailed study regarding the species habits, richness, abundance
and geographical distribution, investigation of regional sites is important.
Study design
The study was conducted from
March 2023 to February 2024 to record the diversity of common and endangered
species. These months were selected for the study so that the diverse kinds of
faunal species can be accessed both during winter as well as summer seasons. In
addition, the selection of this period during the year prevents biases of
vertebrate behaviour towards a particular season. The initial requirement was
the selection of potential sampling sites which was accomplished by rigorous
field survey and perception study of native villagers.
Data source and observation
method
Both the primary and secondary
data sources have been used in this study. In order to obtain primary data,
field observations and documentation of endangered animal species were
conducted, while a critical analysis of potential risks was accompanied.
Quadrat analysis was included as a part of the study to further endorse if the
chosen sampling sites could support the co-existence of different faunal
species which might be endangered species. The data were collected by taking
photographs of indirect evidence like animal footprints, and trails and by
observing quills, faecal matter, and scales. The secondary data sources
included several research articles, reputable websites (i.e., Google Scholar,
Web of Science, Bio One), Wikipedia, Pub Med, and other online sources. Images
of the various species that are accessible have been gathered. For the animal
behavioural study of targeted animals, the selected appropriate time of
investigation was one or two hours after dawn or before sunset as these times
are devoid of much anthropological intervention. The species checklist was
created in accordance with Mandal (2012) and Chattopadhyay et al. (2018).
Public interviews and perception
study
Community interviews are one of
the most well-known and cost-effective methods to determine the distribution of
endangered species (Willcox et al. 2019). The local people can give an idea
regarding the reduction in the number of wild animals
overtime and the probable reason behind it. Local tribal hunters and common
people of surrounding villages of Garh Panchkot hilly region (Baghmara, Rampur,
Lakshmanpur, Aamdanga, Panchut, Ankduara, Gobag, Puapur, and Chalmara) were
interviewed. The information obtained from local villagers were cross-checked
by studying the existing scientific literature. The interviews which have been
taken from local people are generally informal type. Most of the local tribal
communities inhabiting the surrounding villages belong to lower socio-economic
status. The objectives and primary intention of the survey have been clearly
described to the common people. At each site 2–3 h have been invested for the
interview process and the session was continued for 1–2 days in every alternate
week. The studied villages are the homeland of different tribal communities
like Bhumijs, Birhors, Kherias, Lodhas, Mundas, Oraons, Paharias, Santhals and
most of these people are living below the poverty level. They are financially
dependent on hunting in the forest region located nearby the Panchet Hilly
region.
Data collection and analysis
The focus of the current study is
solely on the endangered land vertebrate fauna. Throughout the study period,
pertinent literature was used to identify several vertebrate species. From
previous reports, several sampling techniques were followed in the current
study to achieve the best results because there was no single sampling strategy
that could be used to evaluate the vertebrate diversity fully (Table 1).
All of the study period’s
sampling data was collected from the first week of every month. To document the
diversity and richness of birds, the line transect approach was used. The
topography, roads, and bodies of water (rivers, ponds, & lakes) can all
affect how long the migratory routes of the species under study are. To
evaluate seasonal variations in the richness and number of faunal species,
monthly data from a one-year study were further subdivided into four seasons:
summer (March–May), monsoon (June–August), post-monsoon (September–November),
and winter (December–February). There are certain animals which are not
seasonal but found throughout the year (e.g., Cormorant, Cattle Egret,
Kingfisher, Black Kite, Indian Hare, Common Palm Squirrel, & Indian Flying
Fox).
Capturing photographs
A Nicon Aculon Binocular (A211
10–22 x 50) has been used for close observation of the encountered vertebrate
species and a digital camera
(Nicon D7200 with Nikkor Lens 70–300 mm) has also been used for
capturing their photographs. Photographs
and images are useful for distinguishing between various species. Data were
collected by capturing photographs from the selected sites. Along with the
pictures of different animals, termite mounds, nests, feeding signs on ground
were also collected to trace the existence of different animals (Image 2). Data
were collected during the day time randomly in each week during the studied
period. Although, nocturnal observations were also carried out by using
spot-light, headlight, and three celled torch. The
duration of day along with night time observations was done from 0630 h to 1200
h with a midday break for three to four days in each area. The exact GPS
coordinates were taken using GPS map camera application.
Quadrat method
Quadrat method (25 x 25 m) was
used for analysing the faunal species found in the selected observation sites.
In these places, camera traps were set up for investigation purpose. The data
analysis procedure was repeated at least three times to avoid statistical
biasness. The procedure was performed in the first week of each month and the
minimum interval between two investigations was one month.
Species richness and diversity
were calculated using Biodiversity Pro software (McAleece et al.
1997). The bird species diversity was calculated using the
Shannon-Wiener Diversity index [H′ = ∑ pilnpi]
and Shannon diversity index [Hmax = Log10(S)]. Measurement
of Shannon’s evenness index was calculated using the following formula J =
H′/ Hmax (pi = proportion of total
sample belonging to ith species, S = total number of
species in habitats (species richness) (Magurran 2004).
Ethical permission
The present study was carried out
by following all the instructions of the forest rangers. Some villagers were
involved in the survey and they informed us regarding the availability of local
endangered species. Evidence were also gathered with the help of some forest
officers (anonymised for the sake of research integrity) of the Neturia block
near Garh Panchkot. The participants for the survey were informed thoroughly
regarding the survey goals, in their local languages without using scientific
verbiage and the work was preceded only when they spontaneously consented to
the contribution in the study. The survey-based fieldwork was undertaken and
performed after getting permission from the Raghunathpur Range, Kangsabati
(northern side) Forest division, Purulia, West Bengal.
During the data collection,
special care was taken so that silence could be maintained
and a hassle-free ambience can be prevailed without any major changes after the
investigation. The data collection
method was non-invasive, including field study, camera trapping, quadrat study,
and collection of biological samples. Specific body parts (Quill, scales, skin,
and a few epidermal derivatives) were only collected from the ground when these
were shed off naturally from animal bodies.
RESULTS AND DISCUSSION
Purulia is characterised by many
plateaus and rocky regions and covers an area of forest landscape [Northern
tropical dry deciduous forest (5B/C1c)], with dominant tree species (as per
importance value index (IVI)) Terminalia anogeissiana, Lagerstroemia
parvifolia, Shorea robusta, Terminalia alata, Careya
arborea, Semecarpus anacardium, Lannea coromandelica, Aegle
marmelos, Alangium salvifolium, and Croton persimili (https://www.westbengalforest.gov.in/upload/publication/Garhpanchokot.pdf).
The areas are bounded by the Ranchi and Hazaribag districts of Jharkhand on the
western side, Singhbhum District of Jharkhand on the southern side, and Bokaro
and Hazaribag districts of Jharkhand on the northern side. Garh Panchkot falls
in the Raghunathpur Forest Range of Neturia Block in the Kangsabati (northern
side) forest division in Purulia. The tropic of cancer passes through the
district, so climatic variation can be observed across the line which is the
major reason for the biodiversity of Purulia. The scattered vegetation, bare
earth, and lack of cultivation are the characteristics of the Garh Panchkot
Foothill region. The diversity of vertebrates in the Panchet Hilly region was
previously documented by Chattopadhyay et al. (2018) and according to the
study, with nine species (9%), amphibia had the lowest faunal diversity,
followed by Reptilia (19 species, 18%), Mammalia (11 species, 14%), and Aves
(63 species, 59%). In the present study, special emphasis has been given to
diverse faunal availability in land area with special reference to endangered,
threatened or near threatened organisms. The majority of the species recorded
in this survey fall into the IUCN Red List ‘Least Concern’ category (2017). The
miscellany of land vertebrates in the study area has been depicted in Table 2.
In the present study, 103 different species have been studied with the highest
species diversity observed in class Aves (61 species, 59.23%), followed by
Reptilia (18 species, 17.47%), Mammalia (15 species, 15.56%), and Amphibia
(nine species, 8.73%).
In the Panchet Hilly region, the
Black-headed Ibis Threskiornis melanocephalus and Striped Hyaena Hyaena
hyaena are categorized as ‘Near Threatened’ vertebrate species; the
White-rumped Vulture Gyps bengalensis is listed as ‘Critically
Endangered’ (Table 2).
Amphibians including the Indian
Cricket Frog, also known as the Rice Field Frog (Jijhi byng; Fejervarya
limnocharis), and Indian Burrowing Frog (Gortobasi byng; Sphaerotheca
breviceps) are less commonly found in this hilly region. Moreover, Indian
Common Toad or Kuno byng Duttaphrynus melanostictus, Indian
Bullfrog or Sona byng Hoplobatrachus tigerinus, Common Indian
Tree Frog or Gecho byng Polypedates maculatus, Ornamented
Pygmy Frog or Metho byng Microhyla ornata are found abundantly
[Image 3.1–3.3]. The studied amphibians have been observed in different
microhabitats including open surface, under vegetation, log,
and in burrows.
Among different types of
reptiles, snakes are predominantly found in Garh Panchkot and its surrounding
areas. Russell’s Viper is quite rare although it is found near Kashipur and
Panchet Hilly region. Banded Krait Bungarus fasciatus is regarded as one
of the most venomous snakes which measures about 2.01 m (Bhowmik 2017). Another
poisonous snake is King Cobra Ophiophagus hannah which is obtained
during the study and is categorised as vulnerable on the IUCN Red List due to
gross habitat destruction (Image 3.4). Dhaman Ptyas mucosa is commonly
known as the Oriental Rat Snake; it is a non-venomous species of colubrid snake
(1.5–1.95 m) (Image 3.5). The field study revealed the presence of Indian Rock
Python Python molurus which is believed to be the longest snake (7.3–7.6
m) (Image 3.6). Apart from snake, several other reptiles are found abundantly
in the studied hilly region including Yellow-bellied House Gecko Hemidactylus flaviviridis,
Forest Calotes Monilesaurus rouxii, Asian Chameleon Chamaeleo zeylanicus,
and Common/ Brahminy Skink Eutropis carinata. (Image
3.10–3.12). Here, in this present study, reptiles live in a variety of microhabitats,
including terrestrial, aquatic, and arboreal environments. The observed snakes
have been found from shaded small rocks, leaf litter, rotting logs, temporary
pools, sun exposed rocks.
The avian species biodiversity
depends on the pattern of landscape. The pattern of biodiversity alters with
the climatic conditions, environmental factors, habitats and topography. Though
Purulia is an arid district, there are certain local aquatic bodies including
Saheb Bandh and Kansai River, which provide life support for the aquatic avian
group. Due to the presence of large number of migratory birds, the species
richness value becomes high in winter, especially in Baranti Dam and Saheb
Bandh. According to ebird checklist at Garh Panchkot-Lalpur, 81 species have
been recorded so far, although in the present study 61 species have been found.
The avian food habit is influenced by scarcity of water and the lesser
availability of foods according to seasonal variation. The birds of different
feeding habits including omnivorous (15 species), carnivorous (seven species),
invertivorous (four species), molluscivorous (three species), herbivorous
(three species), granivorous (five species), insectivorous (15 species),
frugivorous (four species), piscivorous (five species) found throughout the
year enforces the fact. Most of the birds existing here are omnivores and
insectivores which might be due to extreme weather condition of Purulia (Mahato
et al. 2021). Among the different local bird species, Cattle Egret (Gobok), Little
Egret (Korchebok), Asian Opened-billed Stork (Shamuk khol), Black-headed Ibis
(Kalomatha kastechara), Red-naped Ibis (Kalo kastehara), Red-vented Bulbul
(Bulbuli), Brown Shrike (Korkota), Oriental Magpie-robin (Doyel), Indian Robin
(Shamya), Purple Sunbird (Moutusi) etc.
are most commonly found whereas migratory birds include Lesser Whistling Duck,
Cotton Pygmy Goose, Northern Pintail, Indian spot-billed duck, Northern
Shoveler, and Greylag Goose (Image 3.13–3.21).
Various types of mammals with
wide range of feeding habit and variable habitat are found during the studied
period. Characteristically few of them exhibit nocturnal habit and adapted for
highly developed eyesight, senses of hearing, and smell, e.g., certain species
of Indian hare Lepus nigricollis, Indian Pygmy Bat Pipistrellus tenuis,
Indian Flying Fox Pteropus medius, Hyena Hyaena hyaena,
House Shrews Suncus murinus whereas considerable number of species
are observed in daytime, e.g., Common Palm Squirrel Funambulus palmarum,
Indian Mongoose Urva edwardsii, and Northern Plains Gray Langur Semnopithecus
entellus. Few of them are carnivorous in nature, like the
Striped Hyaena Hyaena hyaena, Bengal Fox Vulpes bengalensis,
and Jungle Cat Felis chaus which feed on the flesh of
other small animals or remnants of any debris generated from other animals.
During the studied period, mammals have been observed from the vegetation of
ground and canopy cover, rocky caves, underground holes, and crevices (Image
3.22–3.30).
Peafowl Pavo cristatus,
Sloth Bear Melursus ursinus, Common Langur Semnopithecus entellus,
Rhesus Macaque Macaca mulatta, Indian Rock Python Python molurus,
and Fishing Cat Prionailurus viverrinus are among the endangered species
discovered during the current study. The Black-headed Ibis Threskiornis
melanocephalus and Striped Hyaena Hyaena hyaena are classed as ‘Near
Threatened’, whilst the White-rumped Vulture Gyps bengalensis is
designated as ‘Critically Endangered’.
The Black-headed Ibis, or
Oriental White Ibis Threskiornis melanocephalus, is a species of bird in
the ibis family. The head and neck of this species are
black, but its general plumage is white with black, with lengthy legs and a
downward-curving beak. Despite being classified as a wetland species, this bird
can also be found on land that borders wetlands, such as freshwater and
saltwater marshes, reservoirs, lakes, and ponds; it can also be found in rice
fields, recently ploughed crop fields, riversides, urban lakes, and open sewage
gutters (Nandi et al. 2004; Roy et al. 2011; Khan et al. 2016). They often
build their nests during the rainy season, which coincides with their breeding
season. Similarly, another endangered bird species, Pseudibis papillosa,
the Red-naped Ibis, is primarily found in marshes where it lives in flocks. It
is commonly seen in small flocks of 2–4, which could be family groups, and rare
to see larger groups. They have ruby red warty skin on the crown and a usually
dark body with a white spot on the shoulder. It typically stays in pairs during
the breeding season and makes a loud call to entice companions. Usually, they
build their nests atop big trees or power towers (Nandi et al. 2004) (Image 4).
Due to progressive urbanization and developmental activities, the natural
habitats of these birds might be destroyed or degraded. It is observed that the
wetlands are undergoing an unwanted rapid decline in biodiversity due to
climate change, illegal hunting, huge pollution, deforestation, and
eutrophication of wetlands.
With an unfeathered head and
neck, the White-rumped Vulture Gyps bengalensis is a typical
medium-sized vulture. These birds have short tail feathers, a white neck ruff,
and very large wings. The adult’s dark plumage is contrasted with pale features
on the rump, underwing coverts, and back (Grimmett et al. 1998). Like other
vultures, it hunts by flying high in thermals and seeing other scavengers
(Image 4). It primarily feeds on carcasses. Consequently, there are some drugs
(e.g. diclofenac) used for the treatment of livestock (cattle, donkeys) when
they fall ill (Swan et al. 2006). Although, these drugs help the animals feel
better, in majority of the cases, cattle will get sick again. When these
animals die, the diclofenac remains in their system and the vultures who feed
on these animals; they unknowingly swallow the residual drugs which poison the
vultures and causes serious kidney damage (Rana & Prakash 2003).
In general, Striped Hyenas are
slightly smaller than spotted and brown hyenas. They have a big head, thick
nose, large, pointed ears, and black eyes. These are mostly scavengers and
frequently target humans for attack. Male and female Striped Hyenas cooperate
with one another to raise their young, making them nocturnal and monogamous
creatures (Alfred et al. 2002; Biswas et al. 2008) (Image 4). Due to the
scavenging habits, the hyenas are often believed to deplete the livestock. This
causes conflict with local communities and triggers the hunting of hyenas. A
hyena was allegedly killed, beheaded and chopped into pieces by some residents
of Dhanardih Village in Kashipur Block of Purulia in July,
2020. A 15-year-old Striped Hyena was killed by poachers at the Jharbagda
Forest near Manbhum College campus under Manbazar PS area in December,
2013. According to some previous literature reviews, there are nearly 15
contemporary records (2010–2021) in Bengal, from sites situated on the eastern
side of the Chota Nagpur Plateau. These records indicated deaths of hyenas due
to poaching, vehicle accidents, and retaliatory killings (Akash et al. 2021).
According to Chattopadhyay
et al. (2018), striped hyenas were observed from Medinipur-Purulia zone only
once during their study period (two years) and the probable reason for their
decline in number is human-hyena conflict.
According to the most recent
animal census conducted in the forest of southern Bengal, the population of
Indian pangolins Manis crassicaudata has dropped dramatically and 42
pangolins survived in the forest area of Purulia (Samanta et al. 2021). Several
rocky cavities were detected at various places in the Panchkot Hilly region and
surrounding forest areas, where the evidence of Indian pangolin and crested
porcupine sharing their living space were identified. The focal rocky cavity
was found in certain places in hilly forest areas where recent tail,
drag-marks, footprints and claw marks of Pangolins were found [Image 4]. Few
trees were identified (e.g. Karam Neolamarckia cadamba, Bael fruit Aegle
marmelos, Tendu Diospyros melanoxylon) where both pangolins and
porcupines are found in comparatively less number and vulnerable. These animals
prefer to eat fruits, tubers, bulbs, and roots of plants (Sikdar et al. 2024).
As per the native villagers there are several trees (White Siris Albizia
procera, Indian Plum or Kul Ziziphus mauritiana, Banyan Ficus
benghalensis, Palash Butea monosperma, Shisu Dalbergia sissoo)
which are known to be the habitat of several land vertebrates including Spotted
Dove Streptopelia chinensis, Parakeet Psittacula krameri,
Pangolin Manis crassicaudata, Porcupine Hystrix indica, Palm
Squirrel Funambulus palmarum, Gray Langur Semnopithecus entellus,
Indian Flying Fox Pteropus medius, Pygmy Bat Pipistrellus tenuis.
The possible reason for the Indian pangolin Manis crassicaudata and
Indian crested porcupine Hystrix indica becoming endangered is excessive
hunting and poaching for its meat which is consumed by native villagers as well
as tribal communities as delicious food (Hughes 2014). The pangolin scales are
also used for making different types of medicines for promoting blood
circulation, stimulate lactation, cure rheumatisms, and reduce swelling
(Mohapatra et al. 2015; Xu et al. 2016). The WWF has classified pangolins as an
endangered species, marking their status in red ink (Tikadar 1983; WII ENVIS 2017).
Anthropogenic activity has an
impact on the hilly Garh Panchkot Region both directly and indirectly. With the
gradual increase of human population, their caste and religious faith as well
as advancement of living standard, industrialization and urbanization, the
forest range has started reducing and its floral and faunal variety affected
severely. Under the administration of divisional headquarter at Purulia, there
are eight territorial forest ranges (viz. Balarampur, Matha, Bagmundi, Ajodhya,
Jhalda, Kotshila, Joypur and Arsha). The officers and staffs of forest
department are trying to protect the faunal species of Garh Panchkot, but
unable to restore the diversity of vegetation and the old glory of this hilly
region possibly due to lack of proper management strategy and suitable planning
(Raha & Pandey 2015). Moreover, there is a sponge iron factory within a
radius of 100 m and the contaminants are typically deposited on top of the
greenery (Image 5). It has been found that the ash and slag from factories
cover the leaves with a layer of pollutants, which further destroy the delicate
ecological balance and the nutrient cycles.
Moreover, fire is one of the
major threats to wild life. Forest fire causes long-term negative impacts on
faunal species including endangered species and destroys the floral diversity
(trees, herbs, shrubs, grassland). Repeated firework can convert some
shrublands to grasslands whereas fire exclusion transforms grassland into
shrub-land and forest. Fires influence the animals by destroying their
habitats. Generally, the fire season initiates from March/April and continues
up to June (Jhariya & Raj 2014).
In addition to pollution, ancient
tribal hunting festivals (“Shikar Parba”) and cultural events held on the night
of Buddha Purnima (Baishakhi Purnima) are major factors in the extinction of
species. Santhal (local tribe) men wander in the forests and kill wild
porcupines, pangolin, deer, monkeys, wild boar, and bears to acquire meat for
its delicacy, and exoskeleton parts are made into rings to prevent rheumatic
fevers (Banerjee 2022). The illegal hunting and poaching are thought of as a
threat to the avian species. Most of the lakes in the district forest areas are
surrounded by many tribal communities (Mahato et al. 2021). Generally, local
tribal people hunt birds for their mental satisfaction as well as a source of
food. Due to a lack of proper knowledge (literacy rate of Purulia - 64.48 %),
they are not aware of the socioeconomic impact of avian species and the
substantial role of the ecosystem (Mandal et al. 2023). Previously,
Chattopadhyay et al. (2018) reported on the hunting of wild animals from the
Garh Panchkot area. Ritualistic hunting and cultural events have been reported
from the forest area of Jhargram, West Midnaporee, and certain areas of Purulia
(D’Cruze et al. 2024); the migratory bird population of the Purulia District
has declined due to illegal hunting. In extent, Sikdar et al. (2024) reported
tribal hunting of several mammalian species including Indian Pangolin Manis
crassicaudata (Geoffroy, 1803) (Mammalia: Pholidota: Manidae) and Indian
Crested Porcupine Hystrix indica (Kerr, 1792) (Mammalia: Rodentia:
Hystricidae) in Purulia District. Deforestation causes rapid loss of habitat
for migratory bird species (Mahato et al. 2021; Mahato 2021). The tribal
community residing in the villages surrounding the hilly region, abolish the
forest area vigorously. They often depend on the forest not only for fuel and
wood collection but also as the main source of income for their daily life.
Rapid destruction of the forest surrounding the wetland raises uncertainty in
the avian diversity (Image 5).
Eutrophication is another
threatening agent for making the wild fauna (e.g., Cattle Egret, Little Egret,
Asian Open-billed Stork, Black-headed Ibis, Cormorant, Small Kingfisher,
Greater Adjutant Stork) vulnerable. Algal bloom causes discolouration of water
and depletes the oxygen level. In addition, the excessive growth of phytoplankton
resists the sun light penetration beneath the lower depth of the water column
[Image 5E]. Water pollution is now exponentially increased due to human
activities like throwing plastics, garbage and waste food products into water
bodies (Bashir et al. 2020; Wang et al. 2021) (Image 5).
Awareness programme should be
generated regarding the conservation significance of faunal diversity and
natural resources. In the foot hill region of Garh Panchkot, regular
man-wildlife conflict has resulted in death of many wild animals.
Human-elephant negative interactions have been reported previously from Purulia
and Bankura districts due to several developmental activities (Mondal et al.
2016; Das Chatterjee & Mandal 2020). There are more than a few contemporary
records (2010–2021) upon human-hyena from Bengal, from sites specially located
on the eastern limit of the Chota Nagpur Plateau including forest areas of
Purulia District. These records noted around nine deaths due to poaching,
avenging killings, and train accidents (Akash et al. 2021). Regarding this
concern, anthropogenic activity (deforestation, urbanisation,
industrialisation, and hunting) should be checked and well managed. Sanctuaries
and wildlife protected areas should be developed around the Garh Panchkot
region to restore and conserve the entire biodiversity wealth of this hilly
region. The concerned Forest Division should take more protective measures for
preserving wildlife species as per the Schedules of Wildlife (Protection) Act.
1972 (Chakraborty & Kar 2004). Among the different wildlife protective
approaches habitat conservation, wildlife sanctuaries, ex-situ conservation
including zoological parks, botanical gardens, and wildlife safari,
nature-based projects, sustainable land use, wildlife habitat creation, tree
plantation, anti-poaching laws, public education are most important. There
should be some strict management strategies for visitors to conserve the
biodiversity of forests and wetlands. Government should take proper sustainable
and holistic administrative strategies to make the land a plastic-free zone.
The present study is a pioneer
investigation of endangered faunal species of the Garh Panchkot Hilly area and
its surroundings; more research encompassing a wider range of plant and animal
taxa will improve our understanding of the richness of wild species found in
this particular area. The information gathered from this study will be useful
in determining what needs to be done to conserve endangered and near-threatened
species in order to ensure their long-term viability and best interests.
Table 1. Methods used for studying different vertebrate classes
(excluding fishes) from Panchet Hill (‘+’ indicates the method applied for
studying the particular vertebrate class).
|
Method |
Vertebrate class |
|||
|
Amphibia [8.73%] |
Reptilia [17.47%] |
Aves [59.23%] |
Mammalia [15.56%] |
|
|
Hand capturing |
+ |
+ |
- |
- |
|
Extensive searches in
micro-habitats |
+ |
+ |
+ |
+ |
|
Opportunistic spotting |
+ |
+ |
+ |
+ |
|
Call survey |
+ |
- |
+ |
- |
|
Information from local
villagers |
+ |
+ |
+ |
+ |
Table 2. Diversity of land vertebrate species of Panchet hill and
surrounding forests as recorded during the present study.
|
|
Class / Common name |
Local name |
Scientific name |
Authority |
Abundance |
IUCN Red List status |
|
|
Amphibia |
|
||||
|
1. |
Common Indian Toad |
Kuno Byang |
Duttaphrynus melanostictus |
(Schneider, 1799) |
++++ |
LC |
|
2. |
Indian Marbled Toad |
Metho Byang |
Duttaphrynus stomaticus |
(Lütken, 1864) |
++ |
LC |
|
3. |
Indian Cricket Frog or Rice
Field Frog |
Jhinjhi |
Fejervarya limnocharis |
(Gravenhorst, 1829) |
+ |
LC |
|
4. |
Indian Burrowing Frog |
Gortobasi Byang |
Sphaerotheca breviceps |
Schneider, 1799 |
+ |
LC |
|
5. |
Asian Painted Frog |
Rongin Venpu Byang |
Kaloula pulchra |
Gray, 1831 |
++ |
LC |
|
6. |
Ornamented Pygmy Frog |
Chhoto Loubichi Byang |
Microhyla ornata |
Duméril & Bibron, 1841 |
+++ |
LC |
|
7. |
Jerdon's Bull Frog |
Jerdoner Kola Byang |
Hoplobatrachus crassus |
Jerdon, 1853 |
++ |
LC |
|
8. |
Magadha Burrowing Frog |
----- |
Sphaerotheca magadha |
Dinesh, 2019 |
+ |
LC |
|
9. |
Indian Skipper Frog |
Kotkoti Byang |
Euphlyctis cyanophlyctis |
Schneider, 1799 |
++ |
LC |
|
|
Reptilia |
|
||||
|
1. |
Forest Calotes |
Jangli girgiti |
Monilesaurus rouxii |
Duméril & Bibron, 1837 vide Pal et al.,
2018 |
+++ |
NA |
|
2. |
Brook's House Gecko |
Grihabasi tiktiki |
Hemidactylus brookii |
Gray, 1845 |
++++ |
NA |
|
3. |
Indian Flapshell Turtle |
Sundi/chiti kachim |
Lissemys punctata |
Bonnaterre C, 1789 |
++ |
LC |
|
4. |
Peninsular Rock Agama |
Pahari girgiti |
Psammophilus dorsalis |
Gray et al, 1831 |
++ |
LC |
|
5. |
Oriental Garden Lizard |
Baganer girgiti |
Calotes versicolor |
Daudin, 1802 |
++++ |
NA |
|
6. |
Common/Brahminy Skink |
Boro Ghase Anjani |
Eutropis carinata |
Schneider, 1801 |
++ |
LC |
|
7. |
Asian Chameleon |
Bohurupi |
Chamaeleo zeylanicus |
Laurenti, 1768 |
+ |
LC |
|
8. |
Common Indian Monitor |
Go sanp |
Varanus bengalensis |
Daudin, 1802 |
++ |
LC |
|
|
Non- venomous snake |
|
||||
|
9. |
Indian Python |
Ajogor sanp |
Python molurus |
Linnaeus, 1758 |
++ |
NA |
|
10. |
Indian Sand Boa |
Thutu sanp |
Eryx johnii |
Linnaeus, 1758 |
+ |
NA |
|
11. |
Oriental Rat Snake |
Sona dhamna |
Ptyas mucosa |
Linnaeus, 1758 |
++++ |
NA |
|
12. |
Buff-striped Keelback |
Hele sanp |
Amphiesma stolatum |
Linnaeus, 1758 |
++++ |
NA |
|
13. |
Checkered Keelback |
Joldhora |
Xenochrophis piscator |
Schneider, 1799 |
++++ |
NA |
|
14. |
Brahminy Blind Snake |
Telega sanp |
Ramphotyphlops braminus |
Schneider, 1799 |
+++ |
NA |
|
|
Venomous snake |
|
||||
|
15. |
Common Krait |
Chiti sanp |
Bungarus caeruleus |
Schneider, 1801 |
++++ |
NA |
|
16. |
Banded Krait |
Sakhamuti |
Bungarus fasciatus |
Schneider, 1801 |
++ |
LC |
|
17. |
Russell's Viper |
Chondrobora |
Daboia russelli |
(Shaw & Nodder, 1797) |
++ |
NA |
|
18. |
Indian Cobra/ Spectacled Cobra |
Gokhro |
Naja naja |
Cantor, 1836 |
++ |
LC |
|
|
Aves |
|
||||
|
|
Birds of Wetland |
|
||||
|
1. |
Eastern Cattle Egret |
Gobok |
Ardea coromanda |
Boddaert, 1783 |
++++ |
LC |
|
2. |
Little Egret |
Korchebok |
Egretta garzetta |
Linnaeus, 1766 |
++++ |
LC |
|
3. |
Asian Opened-billed Stork |
Shamuk khol |
Anastomus oscitans |
Boddaert, 1783 |
++++ |
LC |
|
4. |
Black-headed Ibis |
Kalomatha
Kastechara |
Threskiornis melanocephalus |
Latham, 1790 |
+ |
NT |
|
5. |
Red-naped Ibis |
Kalo Dochara |
Pseudibis papillosa |
Temminck, 1824 |
+ |
LC |
|
6. |
Little cormorant |
Chhoto pankouri |
Microcarbo niger |
Vieillot, 1817 |
++ |
LC |
|
7. |
Oriental Darter |
Gayar |
Anhinga melanogaster |
Pennant, 1769. |
++ |
LC |
|
8. |
Black-necked Grebe |
Pandubi |
Tachybaptus ruficollis |
Pallas, 1764 |
++ |
LC |
|
9. |
Lesser Whistling Duck |
Chhoto sarali |
Dendrocygna javanica |
Horsfield, 1821 |
++ |
LC |
|
10. |
Small Kingfisher |
Choto machranga |
Alcedo atthis |
Rafinesque, 1815 |
+++ |
LC |
|
11. |
White- breasted/throated
Kingfisher |
Sadabuk/gala machranga |
Halcyon smyrnensis |
Horsfield, 1821 |
+++ |
LC |
|
12. |
Asian Openbill |
Shamuk khol |
Anastomus oscitans |
Boddaert, 1783 |
+++ |
LC |
|
13. |
Greater Adjutant Stork |
Hargila |
Leptoptilos dubius |
Gmelin, 1789 |
++ |
LC |
|
14. |
Great Indian Bustard |
Indian bustard |
Ardeotis nigriceps |
Vigors, 1831 |
++ |
LC |
|
|
Land birds |
|||||
|
15. |
White-rumped Vulture |
Bangla sokun |
Gyps bengalensis |
Gmelin, 1788 |
+ |
CE |
|
16. |
Brahminy Kite |
Sonkhochil |
Haliastur indus |
Boddaert, 1783 |
++ |
LC |
|
17. |
Black Kite |
Chil |
Milvus migrans |
Boddaert, 1783 |
++++ |
LC |
|
18. |
Blue Rock Pigeon |
Jalali kobutor |
Columba livia |
Gmelin, 1789 |
++++ |
LC |
|
19. |
Eastern Spotted Dove |
Tile ghughu |
Streptopelia chinensis |
Scopoli, 1782 |
++++ |
NA |
|
20. |
Red Turtle Dove |
Lal ghughu |
Streptopelia tranquebarica |
Hermann, 1804 |
++ |
LC |
|
21. |
Rose-ringed Parakeet |
Sobuj tia |
Psittacula krameri |
Scopoli, 1769 |
++++ |
LC |
|
22. |
Plum-headed Parakeet |
Fultusi |
Psittacula cyanocephala |
Brisson, 1760 |
++ |
LC |
|
23. |
Spotted Owlet |
Kuture pecha |
Athene brama |
Temminck, 1821 |
++ |
LC |
|
24. |
Eastern Barn Owl |
Lakshmi pecha |
Tyto javanica |
Scopoli, 1769 |
++ |
LC |
|
25. |
Little Swift |
Ghar Batasi |
Apus affinis |
Gray, 1830 |
+++ |
LC |
|
26. |
Indian Roller |
Nilkontho |
Coracias benghalensis |
Linnaeus, 1758 |
+++ |
LC |
|
27. |
Grey Francolin |
Titir |
Ortygornis pondicerianus |
Gmelin, 1789 |
++ |
LC |
|
28. |
Jungle Bush Quial |
Bater |
Perdicula asiatica |
Latham, 1790 |
++ |
LC |
|
29. |
Common Hoopoe |
Mohanchura |
Upupa epops |
Linnaeus, 1758 |
+++ |
LC |
|
30. |
Blue-throated Barbet |
Basanta bouri |
Psilopogon asiaticus |
Lathm, 1790 |
+++ |
NA |
|
31. |
White Wagtail |
Sada khanjan |
Motacilla alba |
Linnaeus, 1758 |
++++ |
LC |
|
32. |
Yellow Wagtail |
Holud khanjan |
Motacilla flava |
Linnaeus, 1758 |
+++ |
LC |
|
33. |
Red-vented Bulbul |
Bulbuli |
Pycnonotus cafer |
Linnaeus, 1766 |
++++ |
LC |
|
34. |
Brown Shrike |
Badami kasai |
Lanius cristatus |
Linnaeus, 1758 |
++ |
LC |
|
35. |
Oriental Magpie-robin |
Doyel |
Copsychus saularis |
Wagler, 1827 |
++++ |
LC |
|
36. |
Indian Robin |
Shamya |
Copsychus fulicatus |
Linnaeus, 1766 |
+++ |
LC |
|
37. |
Purple Sunbird |
Moutusi |
Nectarinia asiatica |
Lathm, 1790 |
+++ |
LC |
|
38. |
Indian Silverbill |
Sormunia |
Euodice malabarica |
Linnaeus, 1758 |
+++ |
LC |
|
39. |
Baya Weaver |
Babui |
Ploceus philippinus |
Linnaeus, 1758 |
+++ |
LC |
|
40. |
Brahminy Starling |
Bamune salikh |
Sturnia pagodarum |
Gmelin, 1789 |
+++ |
LC |
|
41. |
Golden Oriole |
Sonabou |
Oriolus kundoo |
Sykes, 1832 |
++ |
LC |
|
42. |
House Crow |
Kak |
Corvus splendens |
Vieillot, 1817 |
|
LC |
|
43. |
Large-billed Crow |
Darkak |
Corvus macrorhynchos |
Wagler, 1827 |
++ |
LC |
|
|
Migratory birds |
|||||
|
44. |
Green Sandpiper |
Sabuj batan |
Tringa ochropus |
Linnaeus, 1758 |
+ |
LC |
|
45. |
Marsh Sandpiper |
Lariyati |
Tringa stagnatilis |
Bechstein, 1803 |
+ |
LC |
|
46. |
Common Sandpiper |
Cha-pakhi |
Actitis hypoleucos |
Linnaeus, 1758 |
+++ |
LC |
|
47. |
Golden Plover |
Swarna chatar |
Pluvialis fulva |
Gmelin, 1789 |
++ |
LC |
|
48. |
Tufted Duck |
Isti kutum/ Tiki hans |
Aythya fuligula |
Linnaeus, 1758 |
+ |
LC |
|
49. |
Common Pochard |
Bamunia hans |
Aythya ferina |
Linnaeus, 1758 |
+++ |
NT |
|
50. |
Eurasian Wigeon |
Sinthi hans |
Mareca penelope |
Linnaeus, 1758 |
+++ |
LC |
|
51. |
Indian Spot-billed Duck |
Deshi mete hans |
Anas poecilorhyncha |
Forster, 1781 |
+++ |
LC |
|
52. |
Common Moorhen |
Jal murgi |
Gallinula chloropus |
Linnaeus, 1758 |
+++ |
LC |
|
53. |
Cotton Pygmy Goose |
Dhala bali hans |
Nettapus coromandelianus |
Gmelin, 1789 |
+++ |
LC |
|
54. |
Yellow-wattled Lapwing |
Halde gal ti ti |
Vanellus malabaricus |
Boddaert, 1783 |
+++ |
LC |
|
55. |
Red-wattled Lapwing |
Lal gal ti ti |
Vanellus indicus |
Leclerc, 1781 |
+++ |
LC |
|
56. |
Peregrine Falcon |
Baj pakhi |
Falco peregrines |
Tunstall, 1771 |
+++ |
LC |
|
57. |
Marsh Harrier |
Halde khanjan |
Cirus aeruginosus |
Linnaeus, 1758 |
+++ |
LC |
|
58. |
Siberian Rubythroat |
Siberian chunikanthi |
Calliope calliope |
Pallas, 1776 |
++ |
LC |
|
59. |
Northern Pintail |
Lenja hans |
Anas acuta |
Linnaeus, 1758 |
+++ |
LC |
|
60. |
Northern Shoveler |
Pantamukhi hans |
Spatula clypeata |
Linnaeus, 1758 |
+++ |
LC |
|
61. |
Greylag Goose |
Mete raj hans |
Anser anser |
Linnaeus, 1758 |
+++ |
LC |
|
|
Mammalia |
|
||||
|
|
Diurnal |
|
||||
|
1. |
Indian Hare |
Khorgosh |
Lepus nigricollis |
Cuvier, 1823 |
++ |
LC |
|
2. |
Common Palm Civet |
Gondhogokul |
Paradoxurus hermaphroditus |
Pallas, 1777 |
++ |
LC |
|
3. |
Northern Plains GrayLangur |
Hanuman |
Semnopithecus entellus |
Dufresne, 1797 |
+++ |
LC |
|
4. |
Indian Grey Mongoose |
Neul |
Urva edwardsii |
E,Geoffroy Saint-Hilaire,
1818 |
++ |
LC |
|
5. |
Common Palm Squirrel |
Kathbirali |
Funambulus palmarum |
Linnaeus, 1766 |
++++ |
LC |
|
|
Nocturnal |
|
||||
|
6. |
Indian Flying Fox |
Badur |
Pteropus giganteus |
Temminck, 1825 |
++++ |
LC |
|
7. |
Indian Pygmy Bat |
Chamchike |
Pipistrellus tenuis |
Temminck, 1840 |
++++ |
LC |
|
8. |
House Rat |
Idur |
Rattus rattus |
Linnaeus, 1758 |
+++ |
LC |
|
9. |
House Mouse |
Nengti idur |
Mus musculus |
Linnaeus, 1758 |
+++ |
LC |
|
10. |
House Shrew |
Chucho |
Suncus murinus |
Carl Linnaeus, 1766 |
+++ |
LC |
|
11. |
Indian Mole-rat |
Metho idur |
Bandicota bengalensis |
Haerdwicke & Grey, 1833 |
+++ |
LC |
|
12. |
Bengal Fox |
Khaksial |
Vulpes bengalensis |
Shaw, 1800 |
++ |
LC |
|
13. |
Jungle Cat |
Bonbiral |
Felis chaus |
Güldenstädt, 1776 |
+ |
LC |
|
14. |
Striped Hyaena |
Lakra |
Hyaena hyaena |
Linnaeus, 1758 |
+ |
NT |
|
15. |
Indian Crested Porcupine |
Sojaru |
Hystrix indica |
Kerr, 1792 |
+ |
LC |
Abbreviations used: Relative
abundance expressed as +—less abundant | ++++—more abundant | CE—Critically
Endangered | LC—Least Concern | NA—This taxon has not yet been assessed on the
IUCN Red List | NT—Near Threatened. Ref: Raha & Pandey 2015; Chattopadhyay
et al. 2018.
For
images - - click here for full PDF
REFERENCES
Achieng,
A.O., G.B. Arhonditsis, N. Mandrak, C. Febria, B. Opaa, T.J. Coffey, F.O.
Masese, K. Irvine, Z.M. Ajode, K. Obiero, J.E. Barasa & B. Kaunda-Arara
(2023). Monitoring
biodiversity loss in rapidly changing Afrotropical ecosystems: an emerging
imperative for governance and research. Philosophical Transactions of the
Royal Society B 378(1881): 20220271. https://doi.org/10.1098/rstb.2022.0271
Akash, M., A.
Dheer, S.M. Dloniak & A.P. Jacobson (2021). The faded stripes of Bengal: a
historical perspective on the easternmost distribution of the Striped Hyena. European
Journal of Wildlife Research 67(108): 1–12.
https://doi.org/10.1007/s10344-021-01552-9
Alfred,
J.R.B., N.K. Sinha & S. Chakraborty (2002). Checklist of Mammals of
India.Published by Director, Zool. Surv. India, Kolkata. Records of the
Zoological Survey of India Occasional Paper 199: 1–289.
Annual
Administration Report (2021–22). Department of Forest, Government of West Bengal,
217–219 pp.
https://www.westbengalforest.gov.in/publications_administrative_report_banabithi.php
Banerjee, A.
(2022). Bodding’s
Santal Medicine and Connected Folklore vis-à-vis Vidyasagar’s understanding of
Anthropological Study. Journal of the Asiatic Society 63(4): 131–154.
Bashir, I.,
F.A. Lone, R.A. Bhat, S.A. Mir, Z.A. Dar & S.A. Dar (2020). Concerns and threats of
contamination on aquatic ecosystems. Bioremediation and Biotechnology
27: 1–26. https://doi.org/10.1007/978-3-030-35691-0_1
Bhowmik, B. (2017). Studies on biodiversity of snake fauna in Purulia District with special
reference to Garh Panchokot and its surroundings. PANCHAKOTESSAYS
8(2):1–9
Biswas, K.K., P.C. Saren & D.
Basu (2008). Mammalian
and avian fauna of some selected areas of Purulia District, West Bengal. Records
of the Zoological Survey of India 108(3): 59–76.
Chakraborty,
R. & S. Kar (2004). Assessment of habitat as well as avian and mammalian diversiiy in the
Purulia District, West Bengal. Records of the Zoological Survey of India 103
(part–34): 87–124.
Chatterjee,
N.D. & M. Mandal (2020). Human-elephant confict in Panchet Forest Division, Bankura, West
Bengal, India. Gajah 51: 10–15.
Chattopadhyay,
S., S. Dey & S.U. Roy (2018). On the diversity of the vertebrate fauna (excluding
fishes) of Panchet Hill (Garh Panchkot), Purulia, West Bengal, India. Journal
of Threatened Taxa 10(15): 12979–12985. https://doi.org/10.11609/jott.4102.10.15.12979-12985
Chowdhury, S
& S.K. Chowdhury (2020). A study on butterfly diversity and related host plants in Joychandi
Hill of Purulia District, West Bengal, India. IOSR Journal of Environmental
Science, Toxicology and Food Technology (IOSR-JESTFT) 14(10): 55–60.
Das, D.
(2018). Butterfly
(Lepidoptera: Rhopalocera) diversity in relation to habitat utilization at
Jagannath Kishore College, Purulia, West Bengal (India). Journal of Insect
Biodiversity 7(1): 1–16.
D’Cruze, N.,
A. Elwin, S. Ghosh, A.E. Asfaw, E. Coulthard, D. Megson, J. Norrey, S. Giri, V.
Mishra, T. Adhya, S. Chatterjee, M. Banerjee, A. Banerjee & L. Harrington
(2024). Ritualistic
hunts: exploring the motivations and conservation implications in West Bengal,
India. Nature Conservation 56:
243–273. https://doi.org/10.3897/natureconservation.56.132178
Grimmett, R.,
C. Inskipp & T. Inskipp (1998). Birds of the Indian
Subcontinent. Oxford University Press, Delhi, 888 pp.
Hughes, J.E.
(2014). Thinking
(with) the Indian Pangolin: a humananimal perspective on India’s colonial and
princely histories. Nehru Memorial Museum and Library, Teen Murt House, New
Delhi, India, 45 pp.
IUCN (2017). The IUCN Red List of
Threatened Species. Version 2017–3. www.iucnredlist.org. Downloaded
on 26 February 2018.
Jhariya, M.K.
& A. Raj (2014). Effects of wildfires on flora, fauna and physico-chemical properties of
soil—an overview. Journal of Applied and Natural Science 6(2): 887–897.
Khan, T.N.,
A. Sinha & P. Hazra (2016). Population trends and community composition of
migratory waterbirds in three emerging wetlands of global significance in
southwestern Bengal, India. Journal of Threatened Taxa 8(3): 8541–8555.
https://doi.org/10.11609/jott.2652.8.3.8541-8555
Magurran,
A.E. (2004). Measuring
Biological Diversity. Blackwell Publishing, Oxford, 256 pp.
Mohapatra,
R.K., S. Panda, M.V. Nair, L.N. Acharjyo & D.W.S. Challender (2015). A note on the illegal trade and
use of pangolin body parts in India. TRAFFIC Bulletin 27(1): 33–40.
Mahato, S.,
S. Mandal & D. Das (2021). An appraisal of avian species diversity in and around
Purulia Town, West Bengal, India. Journal of Threatened Taxa 13(3):
17906–17917. https://doi.org/10.11609/jott.4733.13.3.17906-17917
Mahato U.
(2021).
Deforestation induced change in subsistence pattern of the Kharia Tribe: a
study from Purulia District. Annals of Anthropological Research and Reviews
1: 86–93.
Mandal, S.K.
(2012). Survey
of wetlands in Puruliya District, West Bengal, with special emphasis
on their macrophytes. PhD Thesis. Department of Botany, The
University of Burdwan, 377 pp.
Mandal, M.,
D. Ghosh, M. Karmakar, S. Mandi, P. Modak, B. Ghosh & D. Mandal (2023). Rural child health in India: the
persistent nature of deprivation, undernutrition and the 2030 Agenda. Environment,
Development and Sustainability 26: 4837–4860.
https://doi.org/10.1007/s10668-023-02912-y
Martínez-Ramos,
M., I.A. Ortiz-Rodríguez, D. Piñero, R. Dirzo & J. Sarukhán (2016). Anthropogenic disturbances jeopardize
biodiversity conservation within tropical rainforest reserves. Proceedings
of the National Academy of Sciences 113(19): 5323–5328.
https://doi.org/10.1073/pnas.1602893113
McAleece, N.,
J.D.G. Gage, P.J.D. Lambshead & G.L.J. Paterson (1997). BioDiversity Professional
statistics analysis software. Jointly developed by the Scottish
Association for Marine Science and the Natural History Museum, London.
Mukherjee,
S.S. & A. Hossain (2024). Assemblage and diversity analysis of butterfly species in relation to
climatic conditions in some tropical habitats: optimization through artificial
neural network model. Journal of Ecology and Environment 48: 44.
https://doi.org/10.5141/jee.24.065
Nandi, N.C.,
S. Bhuinya & S.R. Das (2004). Notes on mid-winter water birds
population of some selected wetlands of Bankura and Purulia District, West
Bengal. Records of the Zoological Survey of India 102(Part1–2): 47–51.
Raha, S.
& S. Pandey (2015). The hunting festival — a serious threat to biodiversity of Ajodhya
Hills, Purulia. Panchakotessays 6(1): 1–7.
Rana, A.K.
& N. Kumar (2023). Current wildlife crime (Indian scenario): major challenges and
prevention approaches. Biodiversity Conservation 32(5): 1473–1491.
https://doi.org/10.1007/s10531-023-02577-z
Rana, G.
& V. Prakash (2003). Cannibalism in Indian White-backed Vulture Gyps bengalensis in
Keoladeo National Park, Bharatpur, Rajasthan. Journal of the Bombay Natural
History Society 100: 116–117.
Roy, U.S.,
A.R. Goswami, A. Aich & S.K. Mukhopadhyay (2011). Changes in densities of water
bird species in Santragachi Lake, India: potential effects on limnochemical
variables. Zoological Studies 50(1): 76–84.
Samanta, S.,
D. Das & S. Mandal (2017). Butterfly fauna of Baghmundi, Purulia, West Bengal,
India: a preliminary checklist. Journal of Threatened Taxa 9(5):
10198–10207. https://doi.org/10.11609/jott.2841.9.5.10198-10207
Samanta, S.,
S. Mahato & A. Mukherjee (2021). Documentation of the globally
threatened Indian Pangolin and its threats from Ajodhya Hills, Purulia, West
Bengal, India. Mammal Tales #36. In: Zoo’s Print 36(12): 65–66.
Sanyal, A.K., J.R.B. Alfred, K.
Venkataraman, S.K. Tiwari & S. Mitra (2012). Status of Biodiversity of
West Bengal. Zoological Survey of India, Kolkata, 969 pp.
Sengupta, A., H. Ogale & E.
Malaiyappan (2021). Euploea sylvester (Fabricius 1793) — Double-branded Crow. In:
Kunte, K., S. Sondhi & P. Roy (eds.). Butterflies of India,v. 3.15. Indian Foundation for Butterflies.
https://www.ifoundbutterflies.org/sp/972/Euploea-sylvester
Sikdar, D.,
S. Bhandari & S. Paira (2024). Coexistence of Indian Pangolin Maniscrassicaudata
(Geoffroy 1803) (Mammalia: Pholidota: Manidae) and Indian Crested Porcupine
Hystrixindica (Kerr 1792) (Mammalia: Rodentia: Hystricidae) in Purulia
District, West Bengal, India. Journal of Threatened Taxa 16(2):
24630–24645. https://doi.org/10.11609/jott.8736.16.2.24630-24645
Swan, G., V.
Naidoo, R. Cuthbert , R.E. Green, D. J. Pain, D.
Swarup D, V. Prakash, M. Taggart, L. Bekker, D. Das, J. Diekmann, M. Diekmann,
E. Killian, A. Meharg, R.C. Patra, M. Saini & K. Wolter (2006). Removing the threat of
diclofenac to Critically Endangered Asian Vultures. PLoS Biology 4(3):
e66. https://doi.org/10.1371/journal.pbio.0040066
Tikadar, B.K.
(1983). Threatened
Animals of India. Zoological Survey of India. Calcutta, 307 pp.
UNEP (2001). India: State of the
Environment 2001. United Nations Environment Programme, Regional Resource
Centre for Asia and the Pacific, Pathumthani, Thailand, xv + 171 pp.
Wang, H., J.
García Molinos, J. Heino, H. Zhang, P. Zhang & J. Xu (2021). Eutrophication causes
invertebrate biodiversity loss and decreases cross-taxon congruence across
anthropogenically-disturbed lakes. Environment International 153:
106494. https://doi.org/10.1016/j.envint.2021.106494
WBFD (2017). West Bengal Forest
Department. http://www.westbengalforest.gov.in/history.php. Accessed
on 29 September 2017.
WII ENVIS
(2017). ENVIS
Centre on Wildlife & Protected Areas.
https://www.wiienvis.nic.in/Database/Protected_Area_854.aspx. Accessed on
29 September 2018.
Willcox, D.,
H.C. Nash, S. Trageser, H.J. Kim, L. Hywood, E. Connelly, G. Ichu, J.K. Nyumu,
C.L.M. Moumbolou, D.J. Ingram & D.W.S. Challender (2019). Evaluating methods for detecting
and monitoring pangolin (Pholidota: Manidae) populations. Global Ecology and
Conservation 17: e00539. https://doi.org/10.1016/j.gecco.2019. e00539
Xu, L., J. Guan, W. Lau & Y.
Xiao (2016). An overview
of pangolin trade in China. TRAFFIC 1–10. Accessed on 28th June, 2024.
https://www.westbengalforest.gov.in/upload/publication/Garhpanchokot.pdf