Journal of Threatened Taxa | www.threatenedtaxa.org | 31
December 2020 | 12(18): 17387–17454
ISSN 0974-7907 (Online) | ISSN 0974-7893 (Print)
doi: https://doi.org/10.11609/jott.6650.12.18.17387-17454
#6650 | Received 02 November 2020 | Final received 17 December
2020| Finally accepted 28 December 2020
On the inadequacy of environment impact assessments
for projects in Bhagwan Mahavir Wildlife Sanctuary and National Park of Goa, India:
a peer review
Girish Punjabi 1,
Anisha Jayadevan 2, Abhishek Jamalabad 3, Nandini Velho 4,
Madhura Niphadkar-Bandekar 5,
Pronoy Baidya 6, Ravi Jambhekar 7, Parag Rangnekar 8,
Omkar Dharwadkar 9,
Rhea Lopez 10, Marishia Rodrigues 11, Farai Divan Patel 12,
H.S. Sathya Chandra Sagar 13,
Sayan Banerjee 14, Manish Chandi 15, Nandini Mehrotra 16,
Shashank Srinivasan 17,
Sneha Shahi 18, Vidyadhar Atkore 19, Nirmal Kulkarni 20,
Gowri Mallapur 21,
Hanuman Gawas 22, Atul Borker 23, Rahul Prabhukhanolkar 24,
Harshada S. Gauns 25,
Dheeraj Halali 26, Vighnesh D. Shinde 27, Katrina
Fernandez 28,
Esme Purdie 29 &
Manoj R. Borkar 30
1 Wildlife
Conservation Trust, 11th Floor, Mafatlal Centre, Nariman Point,
Mumbai, Maharashtra 400021, India.
2 Foundation
for Ecological Research Advocacy and Learning, 170/3, Morattandi, Tamil Nadu
605101, India.
3 H.no. 44,
Kanara House, Mogul Lane, Mahim, Mumbai, Maharashtra 400016, India.
4 Srishti
Manipal Institute of Art, Design and Technology, N5 Campus, CA Site No.21, 5th
Phase, KHB Colony, Yelahanka New Town, Bengaluru, Karnataka 560064, India.
5, 8, 9 Foundation for Environment Research and Conservation,
Vasco, Goa 403802, India.
5,7 Azim
Premji University, PES Campus, Pixel Park, B Block, Electronics City, Hosur
Road, Bengaluru, Karnataka 560100, India.
6, 13 Centre
for Ecological Sciences, 3rd floor, Biological Sciences building,
Indian Institute of Science, Bengaluru, Karnataka 560012, India.
10, 11, 12 MSc Programme in Wildlife Biology & Conservation,
Centre for Widlife Studies, Tata Institute of Fundamental Research, National
Centre for Biological Sciences, GKVK, Bellary Road, Bengaluru, Karnataka
560065, India.
14 National
Institute of Advanced Studies, Indian Institute of Science Campus, Bengaluru,
Karnataka 560012, India.
15 Living
Heritage Foundation, Goa & Andaman Nicobar Environment Team,
North Wandoor, South Andaman, Port Blair,
Andaman & Nicobar Islands 744103, India.
16, 17 Technology
for Wildlife, C13, La Campala Colony, Miramar, Panjim 403001, Goa, India.
18 The Maharaja Sayajirao University of Baroda,
Pratapgunj, Vadodara, Gujarat 390002, India.
19 Forestry
Scholars Society, Near Hanuman temple, Ravi Nagar, Amravati 444607,
Maharashtra, India.
20, 22 Mhadei
Research Centre, 6, Hiru Naik Building, Dhuler, Mapusa, Goa 403507, India.
21 GaiaMitra
Collective Foundation, Aanaa Villa, Lane No 7, PDA Colony, Alto Porvorim,
Bardez, Goa 403521, India.
23 Luta
Innovation, 887/13, Kamat Nagar, Porvorim-Socorro, Goa 403501, India.
24 Mhadei
Research Centre & Indian Bat Conservation Research Unit, Mahalaxmi Plaza, 1st
Floor, RPD cross, Tilakwadi, Belgaum, Karnataka 590006, India.
25 Arannya
Environment Research Organisation, H. Number 7, Near Gram Panchayat, Morlem,
Goa 403505, India.
26 Parvatibai
Chowgule College of Arts & Science, Gogol, Margao, Goa 403602, India.
26, 27 Abasaheb
Garware College, Karve Road, Erandwane, Pune, Maharashtra 411004, India.
28, 29 Wild
Otters Research Pvt Ltd., No. 663/1, Gavona, Tiswadi, Chorao, Goa 403102,
India.
30 Biodiversity
Research Cell, Department of Zoology, Carmel College of Arts, Science &
Commerce for Women, Nuvem,
Goa 403713,
India.
1 girish@wctindia.org
(corresponding author), 2 anisha.jayadevan@gmail.com, 3 abhishek.jamalabad@gmail.com,
4 nandinivelho@gmail.com,
5 nmadhura@gmail.com, 6 titan2ae@gmail.com, 7 ravijambhekar04@gmail.com,
8 rangnekarparag@gmail.com,
9 omkardhr_27@yahoo.co.in, 10 rhealopez168@gmail.com, 11
marishiarodrigues@gmail.com,
12 faraipatel@gmail.com,
13 sathyachandrasagar@gmail.com, 14 sayan.workspace@gmail.com,
15 manish.chandi@gmail.com,
16 nandini@techforwildlife.com,
17 srinivasan.shashank@gmail.com, 18 sneha123shahi@gmail.com,
19 freshwater.biologist@gmail.com,
20 ophidian_nirmal@yahoo.co.in,
21 gowrimallapur@gmail.com, 22 hanumangawas91@gmail.com, 23
borker.atul@gmail.com,
24 pkrahul85@gmail.com,
25 harshada3120@gmail.com, 26 dhirajhalali@gmail.com, 27
vighneshshinde410@gmail.com,
28 katrina@wildotters.com,
29 esme.purdie@hotmail.co.uk, 30 borkar.manoj@rediffmail.com
Editor: Anonymity requested. Date
of publication: 31 December 2020 (online & print)
Citation:
Punjabi, G., A. Jayadevan, A. Jamalabad, N. Velho, M. Niphadkar-Bandekar, P.
Baidya, R. Jambhekar, P. Rangnekar, O. Dharwakar, R. Lopez, M. Rodrigues, F.D.
Patel, H.S.S.C. Sagar, S. Banerjee, M. Chandi, N. Mehrotra, S. Srinivasan, S.
Shahi, V. Atkore, N. Kulkarni, G. Mallapur, H. Gawas, A. Borker, R.
Prabhukhanolkar, H.S. Gauns, D. Halali, V.D. Shinde, K. Fernandez, E. Purdie
& M.R. Borkar (2020). On the inadequacy of environment impact assessments
for projects in Bhagwan Mahavir Wildlife Sanctuary and National Park of Goa,
India: a peer review. Journal of
Threatened Taxa 12(18): 17387–17454. https://doi.org/10.11609/jott.6650.12.18.17387-17454
Copyright: © Punjabi et al. 2020. 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: Manish Chandi
was supported by the Living Heritage Foundation, Bardez, Goa.
Competing interests: As a consultant, Vidyadhar Atkore was part of the
Freshwater fish assessment for the Railway Report by IISc. His contribution to
this paper is independent of the previous affiliation. The other authors declare no competing
interests.
Author details: Girish Punjabi is a Conservation Biologist with the Wildlife
Conservation Trust and is interested in animal distributions, population
ecology, and the role of science in conservation policy. Anisha
Jayadevan is an ecologist working with the Foundation for Ecological
Research Advocacy and Learning (FERAL), India. She currently studies elephant
movement in human-modified landscapes in South India, in the context of
land-use change. Abhishek Jamalabad is a biologist working mainly on marine
ecosystems, but also with terrestrial wildlife of the Western Ghats. He has
been part of avifauna surveys conducted by the Goa Forest Department and the
Goa Bird Conservation Network, and has been a consultant on amphibian surveys
in Karnataka’s Western Ghats. Nandini Velho is Faculty at Srishti
Institute of Art, Design and Technology and completed her PhD in James Cook
University and was an Earth Institute post-doctoral fellow at Columbia
University. Her research interests include studying the interface between
science and society and the human dimensions of wildlife management. Madhura
Niphadkar-Bandekar is a postdoctoral researcher with Azim Premji
University working on mapping land cover change in community-owned forests in
Maharashtra. She is Secretary of the Foundation for Environment Research and
Conservation (FERC) in Goa, a non-profit organization working for environmental
awareness, biodiversity documentation and sustainable tourism in Goa. Pronoy Baidya is a Senior Research
Fellow at the Centre for Ecological Sciences, Indian Institute of Sciences,
Bengaluru, studying ant communities in Goa for his PhD. He is an avid bird-watcher
and the Goa State Reviewer and Editor for ebird, and Vice-President of the Goa
Bird Conservation Network.Ravi Jambhekar is
a visiting scientist at the Centre for Ecological Sciences, Indian Institute of
Science, Bengaluru. He specializes in animal behaviour, community ecology
and effects of habitat fragmentation on animal populations and dispersal. He
combines art and science to make science more accessible to a wider
audience through visual mediums. Parag
Rangnekar is an ecologist with Foundation for Environment Research and
Conservation, Goa. He documents lesser-known fauna, especially butterflies and
dragonflies, and supports conservation action through community
participation. He is an Expert Member on the Goa State Biodiversity Board, Invertebrate
Conservation Information Network for South Asia and Founding President of Goa
Bird Conservation Network. Omkar
Dharwadkar is a professional naturalist for the last 8 years in Goa. He
has added several new records of birds, butterflies, and dragonflies and
discovered a species of dragonfly new to science. He is a Founding Member of
Foundation for Environment Research and Conservation (FERC) and also the
President of Goa Bird Conservation Network.
Rhea Lopez recently
completed her M.Sc. in Wildlife Biology and Conservation from the National
Centre for Biological Sciences. Her dissertation focused on the interaction of
traditional river fisheries with wild piscivores (smooth-coated otters and
mugger crocodiles) along the Mandovi river in Goa. Marishia Rodrigues is currently
finishing her Master’s in Wildlife Biology and Conservation from the National
Centre for Biological Sciences. She also works as an eco-educator with Terra
Conscious and is the hub manager for Conservation optimism India. Farai
Divan Patel is a Master’s student in Wildlife Biology and Conservation
at the National Centre for Biological Sciences, Bengaluru. His Master’s
research has addressed coral reef health in the Lakshadweep. H.S. Sathya Chandra Sagar is a field
biologist and a conservation scientist and Alumnus of CES, IISc. He is
currently a graduate (PhD) researcher at the Sound Forest Lab at the Nelson
Institute, and the Department of Forest and Wildlife Ecology, University of
Wisconsin - Madison, where he is studying the effectiveness of current
conservation practices to protect biodiversity across tropical forests. Sayan Banerjee is a PhD scholar at
National Institute of Advanced Studies, Bengaluru. He works on understanding
behavioural and political ecologies of human-wildlife relations in
North-eastern India in human-dominated mixed-use landscapes. He is also
interested in mainstreaming social sciences in the wildlife conservation
discourse in India. Dr. Manish Chandi was a senior
researcher in Human ecology with the Andaman and Nicobar Environment Team for
25 years, and is currently affiliated with the Living Heritage Foundation. His
interests and work is with human societies and natural resource use and
conservation. Nandini Mehrotra works
as a researcher for a conservation enterprise called Technology for Wildlife.
She is a conservation policy specialist and spatial analyst. She has a BA in
History from St. Stephen’s College and an MPA in Environmental Policy from
Cornell University. Shashank Srinivasan is a conservation geographer and drone pilot. He has
an MRes in Ecology and Environmental Management from the University of York and
an MPhil in Conservation Leadership from the University of Cambridge. He is a
National Geographic Explorer, Chevening Scholar and a Kinship Conservation
Fellow. Sneha Shahi is a conservationist and the UNEP Plastic Tide Turner
Champion, through which brought immense change in Vadodara using an impact
campaign. She led an urban stream restoration which received recognition from
UNICEF, WWF and UNEP. She currently works as an Assistant Director on a project
on the Impact of Linear Intrusions on Wildlife. Dr. Vidyadhar Atkore is based at the Forestry Scholar’s Society in
Amravati, Maharashtra. His interests lie in freshwater ecology and biodiversity
conservation. Nirmal Kulkarni is a herpetologist, field ecologist,
conservationist, and wildlife photographer. He is Director of Wildernest Nature
Resort, an eco-tel in the Chorla Ghats, & Chairman of the Mhadei Research
Centre, Team Lead of Hypnale Research Station, and promoter of HERPACTIVE, a
study initiative on Herpetofauna. Dr. Gowri Mallapur is a Goa-based
veterinarian and wildlife health professional. She is the Director of the
GaiaMitra Collective Foundation based in Goa. She is trained in herpetology,
sustainable development and natural history management. Hanuman Gawas is an MSc in Ecology and
Environmental Sciences from Pondicherry University. He is presently associated
with the Mhadei Research Centre. Atul Borker is a multidisciplinary innovator
and an educator at Luta Innovation. He is the West Asia Coordinator for
IUCN/SSC Otter Specialist Group & the Smooth-Coated Otter Species
Coordinator for the IUCN/SSC Otter Specialist Group. He has been instrumental
in building conservation capacity for otters in Goa. Rahul
Prabhukhanolkar works as a consultant in environment sustainability and
natural resource management in the northern Western Ghats with Mhadei Research
Centre. He has a keen interest in studying Bat ecology and
conservation, and other lesser-known flora and fauna in the region. Harshada S. Gauns is the Founder
President and Treasurer of Arannya Environment Research Organisation in Goa.
She is a trained zoologist with many years of experience in biodiversity
research, community engagement and management planning at the
village-level. Dheeraj Halali completed his B.Sc. in Zoology from
Parvatibai Chowgule College of Arts & Science, Goa. He is currently
enrolled in a Master’s in Biodiversity at Abasaheb Garware College, Pune.
He has a keen research interest in evolutionary ecology, in the evolution of
phenotypes and phenotypic plasticity, anti-predatory strategies, and
life-history. Vighnesh D. Shinde is from Goa and pursuing his MSc.
in Biodiversity from Abasaheb Garware College, Pune. He is interested in the
ecology of dragonflies. Dr.
Katrina Fernandez is interested in various aspects of conservation
biology, including community ecology, population dynamics and population
viability of meso mammals. She also has a strong interest in communicating
conservation issues and science to the public and engaging people in
participatory approaches to conservation. She has worked in Africa, Asia and
Australia. Dr. Esme L. Purdie specialises in Environmental Toxicology,
focussing on natural chemistry and the impacts of pollution throughout the
environment. She is currently affiliated with Wild Otters Research Pvt., Ltd.
(Goa, India) working to conserve the mangrove ecosystem and reduce adverse
human impacts, while also serving as the Science Council Director for the
Organics Council UK. Dr. Manoj R. Borkar is an Associate
Professor & Head, Dept. of Zoology at Carmel College for Women, Goa, for
the last 33 years. He is a Fellow of Indian Academy of Environmental Sciences,
& served on the Goa State Biodiversity Board, Goa State Wildlife Board and
Goa State Experts Appraisal Committee for EIA. He researches arachnids;
especially Tarantulas, Whip Spiders and Whip Scorpions.
Author contribution: All authors contributed to different sections of the
review based on their expertise. The manuscript was compiled and edited by
Girish Punjabi, Anisha Jayadevan, Abhishek Jamalabad, Nandini Velho, Madhura
Niphadkar-Bandekar, and Pronoy Baidya.
Acknowledgements: Meghna Agarwala is thanked for critical comments which
improved the manuscript. Akshatra Fernandes is thanked for help with collating
the checklist of plants.
Abstract: The Environment Impact Assessment (EIA) is a
regulatory framework adopted since 1994 in India to evaluate the impact and
mitigation measures of projects, however, even after 25 years of adoption, EIAs
continue to be of inferior quality with respect to biodiversity documentation
and assessment of impacts and their mitigation measures. This questions the credibility of the
exercise, as deficient EIAs are habitually used as a basis for project
clearances in ecologically sensitive and irreplaceable regions. The authors reiterate this point by analysing
impact assessment documents for three projects: the doubling of the National
Highway-4A, doubling of the railway-line from Castlerock to Kulem, and laying
of a 400-kV transmission line through the Bhagwan Mahavir Wildlife Sanctuary
and National Park in the state of Goa.
Two of these projects were recently granted ‘Wildlife Clearance’ during a
virtual meeting of the Standing Committee of the National Board of Wildlife
(NBWL) without a thorough assessment of the project impacts. Assessment reports for the road and railway
expansion were found to be deficient on multiple fronts regarding biodiversity
assessment and projected impacts, whereas no impact assessment report was
available in the public domain for the 400-kV transmission line project. This paper highlights the biodiversity
significance of this protected area complex in the Western Ghats, and
highlights the lacunae in biodiversity documentation and inadequacy of
mitigation measures in assessment documents for all three diversion
projects. The EIA process needs to
improve substantially if India is to protect its natural resources and adhere
to environmental protection policies and regulations nationally and globally.
Keywords: Biodiversity, development, highway, National Board for
Wildlife, protected area, railway, transmission line, Western Ghats.
Abbreviations: Bhagwan Mahavir Wildlife Sanctuary and National
Park—BMWS & NP | EC—Environmental Clearance | EIA—Environment Impact
Assessment | FC—Forest Clearance | IUCN—International Union for Conservation of
Nature and Natural Resources | NP—National Park | PAs—Protected Areas | WC—Wildlife
Clearance | WPA—Wildlife (Protection) Act | WS—Wildlife Sanctuary |
MoEFCC—Ministry of Environment, Forests and Climate Change, Government of India
| UNESCO—United Nations Educational, Scientific & Cultural Organization.
1. BACKGROUND
The Environment Impact
Assessment (EIA) process is a standard framework for appraisal and evaluation
of development projects. The first EIA
notification in India was published in 1994 by the Ministry of Environment and
Forests. This was followed by a new EIA
notification in 2006 that made it mandatory for most projects in the mining,
power, infrastructure, and industrial sectors to seek Environmental Clearance
(EC) prior to new developments or the expansion of existing ones. If a project is sited in a protected area or
passing through a notified forest it may additionally require a Forest
Clearance (FC) and/ or Wildlife Clearance (WC).
While India has been following the EIA process for over 25 years,
studies have frequently highlighted sub-standard and deficient EIA and other
assessment reports used by proponents to obtain these clearances by diluting
the spirit of the exercise (Comely 2018; Datar et al. 2019; Sheth et al. 2020).
EIA and other assessment
reports have often been found deficient in documenting biodiversity, assessing
direct, indirect, and cumulative impacts, and proposing mitigation measures
(Datar et al. 2019; Khera & Kumar 2010; Sheth et al. 2020). In this Review, the authors present an
analysis on three projects that will cumulatively affect Bhagwan Mahavir
Wildlife Sanctuary and National Park (BMWS & NP), formerly known as Mollem,
in the state of Goa (Figure 1, Image 1–3).
These forests are an important part of a larger landscape that affords
connectivity not only to other forests in Goa but also across the border to
Kali (Dandeli-Anshi) Tiger Reserve in Karnataka. The three projects are as follows:
a. Road: The four-laning of the
National Highway 4A (153km in total length, of which 70.07km falls within Goa,
with 13km bisecting the BMWS & NP, now redesignated as National Highway
748), that is being carried out by the National Highways Authority of India and
by the Public Works Department in Goa.
The proposal involves the diversion of about 31.015ha of protected
forest area (24.265ha in the NP and 6.75ha in the WS). At present, the road passing through the
protected area has a 7m wide two-lane carriageway. The proposal involves widening specific
sections of the road, thus creating new intrusions into the forest that have
not yet faced the direct and indirect impacts of fragmentation. On the other side of the border in Karnataka,
the highway expansion passing through the protected area (PA) has been halted
by the Karnataka High Court. The total
forest land required is 63.615ha and the total number of trees to be felled are
20,340, of which 12,097 trees will be felled from the PA.
b. Railway: The second project is the
doubling of the Castlerock–Kulem railway line, which is part of the larger
Hospet–Tinaighat–Castlerock–Kulem–Madgaon–Vasco line. The total length of this railway line is
345km, of which 26km passes through the BMWS & NP, that is being undertaken
by MS Rail Vikas Nigam Ltd. The total
forest land required is 138.37ha and the total number of trees to be felled are
22,882; of which 20,758 will be felled from the PA. Four underpasses measuring 12m in width and
5.65m in height have been proposed as mitigation measures along the railway
line. The existing railway line from
Hospet to Vasco was laid in 1900 and presently connects iron ore mining and
industrial areas in Hospet to Mormugao Port in Vasco. The alignment of the second proposed railway
line runs parallel to the existing line and passes through forest tracts in and
around Kali Tiger Reserve and in the BMWS & NP.
c. Transmission line: The third project is the
laying of a 3.15km transmission line through BMWS & NP. The line will be set between Narendra,
Karnataka and terminating with a 400 kV substation at Xeldem, Goa. This project is being undertaken by M/s Goa –
Tamnar Transmission Project Ltd (Sterlite Power) with 12,097 trees that will be
felled and 11.54ha of forests being diverted, with the power line being 46m in
width. The project also requires
diversion of 30.412ha of protected forests of Kali Tiger Reserve in Karnataka. In reality, there are five forest diversion
proposals for one single project involving diversion of total 323.596ha of
forest land through the state of Goa (146.505ha) and the state of Karnataka
(177.091ha). The entire project in the
state of Goa would require felling of 43,456 trees and felling of another
62,289 trees in the state of Karnataka.
The total trees enumerated to be felled for implementing the entire
inter-state project is 1,05,745 trees.
The Indian Ministry of
Environment, Forests and Climate Change (MoEFCC) has a web portal, Parivesh,
which makes public all project documents required for clearances sought by
project proponents. The Parivesh website
does not have the Biodiversity Impact Assessment Report of the transmission
line project uploaded (as on 1 July 2020), despite in-principle approval being
afforded at the 57th National Board for Wildlife meeting held on 7
April 2020.
In this Review, we first
present the biodiversity significance of BMWS & NP by reviewing published
literature on taxonomic groups, and referring to unpublished sources such as
dissertations, reports, and checklists that have been at least peer-reviewed
among expert groups, where published information is scarce. We then present a critique of the two
assessment studies (the railway study prepared by the Indian Institute of
Science, Bengaluru and the highway study prepared by Aarvee Associates,
Hyderabad) and a summary on the impact of the transmission line given that the
project report is not available in public domain.
2.
ABOUT BHAGWAN MAHAVIR WILDLIFE SANCTUARY AND NATIONAL PARK
Bhagwan Mahavir Wildlife
Sanctuary and National Park comprises wet evergreen, semi-evergreen, and moist
deciduous forests in the Western Ghats.
Both PAs are contiguous and span an area of 240km2, with
133km2 as WS and 107km2 as NP.
Both PAs are classified as
Important Bird and Biodiversity Area by the Bombay Natural History Society and
Birdlife International, UK (Rahmani et al. 2016).
A summary of the known
status of taxonomic groups is provided here to enable a reliable assessment of
the ecological value of the PA complex (Image 4).
2.1
Plants and Fungi
BMWS & NP comprise
more than 700 plant species (Datar & Lakshminarasimhan 2013; See Appendix
II). Of these, at least 127 species are
endemic, making about 18% of the total flora (Datar & Lakshminarasimhan
2011).
The region is a hotspot
for fungal diversity in the Western Ghats.
Nearly 1,200 fungi species are known from Goa, of which at least 500
mushroom species have been identified and many are yet to be described
(Nandkumar Kamat in litt. 27.xii.2020).
A total of 18 lichen species are known from the PA, although the overall
diversity is likely to be higher.
2.2
Insects and Arachnids
Both PAs together support
219 butterfly species (Appendix V) and 80 species of odonates (Appendix VI), of
which 14 species of butterflies and 18 species of odonates are endemic to the
Western Ghats. Two odonate species Idionyx
gomantakensis (Subramanian et al. 2013) and Cyclogomphus flavoannulatus
(Rangnekar et al. 2019) have been described from within and immediate outskirts
of the PA. A few butterfly species found
in the BWWS & NP such as the Danaid Eggfly Hypolimnas misippus,
Common Mime Papilio clytia, Common Pierrot Castalius rosimon,
Blue Nawab Polyura schreiberi, Kanara Oakblue Arhopala alea,
Orchid Tit Hypolycaena othona, Short-banded Sailor Neptis columella,
and Crimson Rose Pachliopta hector are protected under Schedule I of the
Wild Life (Protection) Act, 1972 (henceforth WPA 1972). Two endemic butterfly species found here are
the Malabar Rose Pachliopta pandiyana and the Southern Birdwing Troides
minos. A 2011 report on moth
diversity from the northern Western Ghats reports at least 418 moth species out
of which 116 species were unidentified, and potentially new to science
(Shubhalaxmi et al. 2011). A total of 75
ant species are recorded from the WLS of which seven are endemic (See Appendix
IX). Six scorpion species, 16 spider
species, and one species each of Whip Scorpion and Whip Spider have been
recorded from both the PAs (Bastawade & Borkar 2008). An isolated population of Whip Spider Phrynichus
phipsoni and Whip Scorpion Labochirus tauricornis occurs in the
proximity of this PA (Borkar et al. 2006; Borkar 2018).
2.3
Fish
The Western Ghats supports
over 300 fish species of which more than 65% are endemic (Kumar & Devi
2013). New fish species and range
extensions are being described from this region as yet, suggesting that fish
species assessments and distribution patterns remain incomplete (Molur et al.
2011). A comprehensive study in the
Mhadei sub-basin (which includes BMWS & NP) has the presence of 49 fish
species, of which 18 species are endemic to the Western Ghats (Atkore 2017; See
Appendix IV).
2.4
Herpetofauna
The reptilian diversity of
the region is represented by 52 species from Crocodylidae (Crocodiles),
testudines (freshwater turtles & tortoises), and squamates which includes
Sauria (Lizards) and Ophidia (Snakes) (See Appendix VII). Amongst the diversity of reptiles, the Indian
Rock Python Python molurus, Indian Monitor Lizard Varanus bengalensis,
and King Cobra Ophiophagus hannah are some species in the Schedule I and
II of WPA, 1972. Other endemics such as
the Malabar Pit Viper Trimeresurus malabaricus and the Large-Scaled
Shieldtail Uropeltis macrolepis are also reported from the region.
In the past 15 years, 112
new amphibian species have been discovered from the Western Ghats, indicating
high species richness and a need for more systematic studies in the
landscape. Among the 218 known species
of amphibians, 87.8% (158 species) are endemic to the Western Ghats (Nirmal
Kulkarni pers. obs. 01.vii.2020). The
two PAs together contain at least 36 amphibian species (See Appendix VIII). Castlerock is the type locality of Nyctibatrachus
petraeus (Das & Kunte 2005) and Raorchestes bombayensis
(Annandale 1919). Biju et al. (2014a)
described 14 new dancing frogs, of which one species Micrixalus uttaraghati
is found in the streams that cut across the existing Castlerock-Kulem railway
line. Similarly, these streams are home
to Indosylvirana caesari and Indirana chiravasi, two new frog
species that were described recently (Biju et al. 2014b; Padhye et al.
2014). Seven new amphibian species have
been discovered in the past two decades from Goa.
2.5
Birds
The first ornithological
study in Goa was conducted by Grubh & Ali (1976). During their 16-day survey that included
Mollem, the team recorded a total of 97 bird species. Presently, 286 species have been recorded
from the BMWS & NP (Rahmani et al. 2016; see Appendix I). The list includes species such as the
Critically Endangered Indian Vulture Gyps indicus, Endangered Egyptian
Vulture Neophron percnopterus and other globally threatened species such
as the Lesser Adjutant Leptoptilos javanicus, Woolly-necked Stork Ciconia
episcopus, Nilgiri Wood Pigeon Columba elphinstonii, and Malabar
Pied Hornbill Anthracoceros coronatus.
A total of 14 bird species recorded from BMWS & NP are endemic to
the Western Ghats and 32 of the recorded species are listed in the Schedule I
(Part III) of the WPA, 1972. Six bird
species are classified as Near Threatened by International Union for
Conservation of Nature and Natural Resources (IUCN).
2.6
Mammals
BMWS & NP, along with
the Kali Tiger Reserve and surrounding reserved and protected forests cover an
area of at least 2,000km2 and form an important Bengal Tiger Panthera
tigris habitat (Gubbi et al. 2016).
The National Tiger Conservation Authority has recommended bringing
together the protected areas of Goa and Karnataka for Tiger conservation and
improved management. In a document
released by the MoEFCC titled “Connecting Tiger Populations for Long-term
Conservation” the forests of Goa are mentioned as one (Sahyadri-Radhanagari-Goa)
of 32 major Tiger corridors in India. A
breeding population of Tigers has been recorded from the tri-junction of
Goa–Karnataka–Maharashtra (Girish Punjabi pers. obs. 19.iii.2019; Jhala et al.
2020). In May 2019, the Forest
Department of Goa photographed an individual Tiger using trail cameras in the
BMWS & NP, and expect more individuals to be present (The Goan Everyday
2019). On the 5 January 2020, carcasses
of four Tigers – a female and her three cubs were found in the neighbouring
Mhadei Wildlife Sanctuary (Kerkar 2020).
The four tigers were poisoned in retaliation for depredating livestock
(Kerkar 2020).
More than 60 mammal
species are likely to occur in the PAs, of which 11 species belong to Schedule
I of the WPA 1972 (See Appendix III).
Gad & Shyama (2009) found that Gaur Bos gaurus was widespread
and fed on 32 plant species belonging to 17 plant families in the PA. Sengupta & Radhakrishna (2013)
encountered a higher number of Bonnet Macaques Macaca radiata in BMWS
& NP as compared to other parts of Goa.
Krupa et al. (2017) reported two sympatric otter species, the Asian
Small-clawed Otter Aonyx cinereus and Smooth-coated Otter Lutrogale
perspicillata in the buffer region of Mhadei WS, which adjoins BMWS &
NP.
3.
REVIEW OF EIA FOR THE NH-4A HIGHWAY EXPANSION PROJECT
After compiling lists of
taxonomic groups known from the PAs, the authors reviewed the EIA for NH-4A
Highway Expansion (henceforth Road Report) for information provided on
taxonomic groups, environmental and social impacts of the project. We found inadequacies in most aspects and as
such the Road Report was observed to be of poor quality. The relevant issues are discussed here.
3.1
Plants
i) Several issues were
found with the reported methodology for the baseline survey on plant species in
the Road Report. The sampling strategy
was not clearly indicated. The Report
says that the number of quadrats in each habitat type was proportionate to the
land in the habitat type, but no further information is provided whether a
randomized or systematic sampling protocol was used. In the absence of a protocol, sampling
locations would be biased and not fully representative of the habitat type.
ii) Resultantly, the list
on floral species in the Road Report is inadequate when compared to existing
species list of the area (Datar & Lakshminarasimhan 2011).
iii) The sampling
methodology outlined was likely not followed.
The data were finally compiled and based on a reconnaissance trip and
secondary literature (Section 5.8.2, Page 79).
No analysis of species diversity or dominance were performed, and the
findings are only provided in the form of a brief species list (Table 5.15,
Page 79). This list excludes understory
species, herbs, and lianas. No data are
presented on tree girths, size classes or age structure, which could help in an
assessment of the damage to the forest.
iv) The Road Report is not
clear about which agency will plant trees as part of the project and the
figures provided are inconsistent. It
states that the intention is to plant 20,000 avenue trees next to roadside
parking areas, toll gates, bus bays, and truck lay-bys (page 82). The Report later revises this number to
50,000 trees (Page 96), then to ~27,000 trees (based on planting 333 trees per
km2 in wildlife sanctuary and 666 trees per km2
elsewhere) and finally back to 20,000 trees (Page 137).
v) The Road Report has
also not specifically identified plant species that will provide appropriate
and compensatory ecosystem services for the tree plantation. The species to be planted on the edge of the
highway are Mahua Madhuca longifolia and Khair Acacia catechu,
which are not typical of the Western Ghats and Bougainvillea sp., an ornamental
that is not native to India, but is to be planted in the median.
3.2
Insects and Arachnids
i) The Road Report has no
impact assessment of linear intrusions on insect and arachnid diversity, with
no details on species richness in the area.
No attempt has been made to compile secondary information from published
and unpublished sources.
ii) There are many studies
from India and the world which have examined the impact of roads on
insects. Insects suffer a high mortality
while crossing roads or may avoid crossing roads altogether (Muñoz et al.
2015). Studies report that vehicle
lights attract many insects, causing mortality during the night (Seshadri &
Ganesh 2011). The barrier effect of
roads is higher for slow-moving insects (Muñoz et al. 2015), but even flying
insects such as butterflies are affected by fragmentation created by roads, as
the nature of patch-edge affects their dispersal ability (Ries & Debinski
2001; Dover & Settele 2009). Studies
on grasshoppers have demonstrated that males increase their call frequency in
response to road noise, which may have population-level consequences (Lampe et
al. 2014).
iii) Despite evidence of
high levels of diversity and endemism in the BMWS & NP, odonates have not
been surveyed. Species of hill streams
are more narrowly-distributed and are indicators of water quality (Simaika et
al. 2016). A new dragonfly species Idionyx
gomantakensis (Subramanian et al. 2013) was reported in 2013 from the PAs,
a fact that has been overlooked in the Road Report. This raises doubts whether secondary data has
been reviewed while compiling the faunal list for the project area.
iv) No details are
provided for Arachnids in the Road Report.
In so far as the amblipygid, urropygid, and theraphosid spiders of these
areas are concerned, given their fidelity to their habitat type and their
rather restricted movement, any alteration of the habitat, due to road
construction and widening, shall decimate these small and isolated populations
beyond recuperation and renewal, even leading to local extinctions
(Maelfait & Hendrickx 1998).
3.3
Fish
i) No fish species or
impacts of road expansion have been described in the Road Report. It states that “since most of the water
bodies remain dry during the non-monsoon months, this [sediment] impact will be
negligible” (Page 98). This
statement is inaccurate, as several perennial streams and pool habitats contain
water and act as refuges for various fish species in the non-monsoon
months. A study cautions against the
effects of sedimentation and run-off on the fish communities due to rampant
vehicular traffic in the neighbouring Mhadei Sanctuary (Atkore 2017).
ii) Many other impacts are
envisioned which the Road Report has not assessed. Soil erosion due to the removal of riparian
vegetation would have short-term as well as long-term impacts on stream
dwelling communities. Riparian
vegetation plays an important role in maintaining ambient temperature in the
headwater catchment (region from numerous streams originates) enabling
persistence of diverse, endemic and habitat specialist fish species such as Balitora
sp., Glyptothorax sp., Schistura sp., Bhavania sp., and Garra
sp. (Sreekantha et al. 2007).
iii) Increased soil
erosion due to the road expansion is likely to multiply the sedimentation load,
which may impair water quality greatly due to high turbidity. Sediment deposition is likely to reduce food
availability to aquatic communities.
Bottom-dwelling fish such as Balitora sp., Glyptothorax
sp., and Schistura sp. feed on benthic insects (Daniels 2002), and have
a very narrow range of distribution and tolerance level to certain water
quality variables.
iv) Higher suspended
solids and silt deposition can also affect spawning grounds and various life
stages of fish. A few highly sensitive
fish species such as Deccan Mahseer Tor khudree and Hypselobarbus
sp. are known to migrate upstream for feeding and breeding, either once or
twice a year. Mahseer, in particular,
are known to choose definite and special spawning grounds which usually are
rich in dissolved oxygen content, neutral pH, and cool water temperature. Eggs, fry and fingerlings stages of this fish
are highly sensitive to the slight alterations in their environment and
spawning habitats (Daniels 2002). Soil
erosion and high deposition of silt along with stream flow are expected to
destroy their habitat, and could reduce their population in Dudhsagar and other
adjoining waterbodies.
v) Surface dwelling fish
such as Devario sp., Barilius sp., and Salmostoma sp. feed
largely on insects falling from the canopy (Johnson & Arunachalam
2010). Higher turbidity due to sediment
load would reduce their ability to forage and may restrict these fishes to
downstream habitats, affecting their survival.
3.4
Herpetofauna
i) Details on
herpetofaunal diversity in the PAs is not mentioned in the Road Report. Section 5.8 (Page 74) mentions that Goa has a
high snake population. While this may be
a general statement, it is not backed by any references.
ii) Further, data from
exsiting literature points to an increase in the number of snake and amphibian
road-kills with existence of roads (Garriga et al. 2012; Santhoshkumar et al.
2017). There is, however, no mention of
the impact of road expansion on herpetofaunal diversity of the PA in the Road
Report.
3.5
Birds
i) Although the Road
Report mentions that a field survey has been carried out (Section 5.8.2 (v),
Page 78), there is no bird checklist provided, except for one mention of the
Indian Robin Copsychus fulicatus along with other fauna (Table 5.16,
Page 82). Bird species richness and
abundance were not quantified in the project area that may be affected due to
the project construction. This is a
serious shortcoming given that 286 bird species have been recorded in the BMWS
& NP (Rahmani et al. 2016, See Appendix I).
ii) A section (Page 74) of
the Road Report matches the Wikipedia page “Flora and Fauna of Goa” (Wikipedia
contributors 2020), which mentions that the state bird of Goa is “the
Ruby-throated Yellow Bulbul, which is a variation of Black-crested
Bulbul”. This is inaccurate, as the
state bird of Goa is the Flame-throated Bulbul Pycnonotus gularis, which
recent studies have elevated to a full species (Rasmussen & Anderton
2012).
iii) There is further
confusion about the state bird of Goa; section 5.8.1 of Page 78 of the Road
Report refers to the Yellow-throated Bulbul Pycnonotus xantholaemus as
the state bird. The Yellow-throated
Bulbul is endemic to peninsular India and has no known distribution in
Goa. The faunal statistics presented in
section 5.8.1 have been taken from Kumar & Somashekar (2008) with no
attribution to the original source. The
absence of any data on birds, either quantitative or qualitative, from an area
that has been classified as an Important Bird and Biodiversity Area (IBBA),
undermines the purpose of the EIA.
3.6
Mammals
i)
To assess faunal diversity, field surveys and a local consultation were
conducted in the Road Report, however, it does not contain any methodological
specifications or sampling strategy.
Sampling methods for different taxa are also not clearly differentiated. The species list is limited with only 16
species recorded. This is a clear
underestimate as more than 60 mammal species are known to inhabit this region
(See Appendix III).
ii)
The presence of the Bengal Tiger in the area is also not mentioned. The report states that no endangered species
are found in the area which is clearly misleading considering three Endangered
mammal species occur, including the Tiger, Dhole, and Indian Pangolin. One of the species mentioned in the Road
Report, the Red Giant Flying Squirrel Petaurista petaurista is not found
in the Western Ghats. Common species
such as the Bonnet Macaque and Chital Axis axis, are also not
reported.
iii)
The Road Report states that the road expansion will not affect faunal species,
and instead claims that species “may increase in number because of the road
structures as the project will not obstruct their movement rather can create
new habitats for them” (Section 5.8.1, v, Page 82). This statement is misleading as wide roads
are known to create an obstruction to movement for a wide variety of species,
including mammals (Bennett 2017). Roads
also create forest edges that can harmfully affect native vegetation and rare
wildlife due to edge effects, which extend far beyond the area of the road (Gubbi
et al. 2012; Poor et al. 2019). Small
mammal communities near roads have also been found to differ from those away
from roads (Goosem 2002).
iv)
Section 5.8.1 (Page 78) of the Road Report mentions the Leopard and Black
Panther as two separate species, however, these are colour morphs of the same
species Panthera pardus. The Gaur
Bos gaurus, which is the State Animal of Goa, does not find mention in
the checklist. Section 5.8.1, (v) also
states that none of the faunal species found here are “endangered or
extinct”. This is unsound as endangered
species such as the Bengal Tiger, Dhole, and Indian Pangolin are found in the
region, while extinct species are found nowhere in the wild.
3.7
Land-use
i) A land-cover map for
this project was acquired as a secondary data source, without clarity on how it
was prepared. The map presented is for
the entire state of Goa (Figure 5.23, Page 75), and not specific to the project
site. The impacts on the land-use and
land-cover specific to the project area have not been assessed in the EIA. The land-use table (Table 5.14, Page 73) has
an error in summation of all land-use types.
Further, the land-cover classes in the table do not match the ones in
the map. These errors create confusion
about which land-cover types will be affected by the project.
3.8
Water
i) The Road Report
mentions that there are declining water level pockets in South Goa, indicating
the need to strictly regulate groundwater extraction in these pockets, however,
Section 5.1.4. (Page 40) of the Report has insufficient information on the
river basins in the region. Only water
depths are provided, without any data on the coverage area, volumes, or a
reasonable level of water extraction that is possible from rivers during road
expansion.
ii) Section 5.5.1. (Page
51) states that chloride concentrations are “well within the desirable and
permissible limits”. This statement is
misleading. Samples GW-02 and -06 both
had detected values above the desirable limit range and are at risk of
exceeding the Bureau of Indian Standards’ drinking water standards. Thus, there is insufficient evidence to
support the statement that there is ‘good’ scope for groundwater exploitation
in all the five affected taluks in the South Goa District.
iii) There is inadequate
information on the water assessment sampling procedure in the region. Section 5.5.1 (Page 51) suggests that single
samples were collected from five separate surface water sites and eight
separate groundwater sites, during one sampling visit. No indication of the season or sampling date
is provided, nor of repeated sampling to ensure accuracy or reliability. The statement that “total hardness observed
to be constant in all samples” is flawed, as notable variation was observed
between hardness in the different sample locations of the Road Report.
3.9
Air
i) Air quality would be
negatively affected after the road expansion, but there is scarce attention
paid to any robust evaluation in the Road Report. The statement that with the “proposed
four-laning project, traffic may further come down and ease the vehicles
movement and traffic congestion, which may lead to reduce the pollution levels”
lacks substantial evidence and cannot be a justification for road expansion
within a PA and ecologically-sensitive area.
ii) Table 6.5 (Page 102)
proposes that greenhouse gases and other pollutant emissions may be
significantly reduced based on the assumption of a small increase in traffic
burden along with the avoidance of stopping, idling and congestion, however,
traffic projections in the report show that total traffic is projected to only
increase over the years, at all the three points where present traffic was
surveyed (Table 2.15, Page 20). It is
doubtful that vehicular emissions will be reduced with increased number of
lanes, when scientific literature indicates that road widening leads to
increased emissions which negatively affect air quality (Roberts et al. 2010;
Font et al. 2014)
3.10
Soil
i) According to Table
5.13. (Page 72) of the Road Report, among the trace metals likely to
contaminate soils due to large-scale construction and traffic pollution, only
Lead (Pb) and Iron (Fe) are noted, however, this is this is insufficient, as
several heavy metals such as Cadmium (Cd), Copper (Cu), Zinc (Zn), and
Manganese (Mn) originate from material abrasion, fuel combustion and road dust
(Chen et al. 2010; Abdel-Latif & Saleh 2012; Świetlik et al. 2013). Heavy metals have been associated with high
levels of genotoxicity and mutagenicity in soils contaminated with heavy metals
(Husejnovic et al. 2018) and their concentrations should be monitored and
potentially reduced in PAs, particularly in view of the risk of trophic
transfer, migration, and bioaccumulation (Zhang et al. 2018; Chouvelon et al.
2019).
3.11
Social Impacts
i) Datar &
Lakshminarasimhan (2011) documented around 90 floral species to be important
for local consumption and livelihood.
While the Road Report lists flora of the affected area and people’s
reliance on non-timber forest produce (NTFP), it does not mention the potential
impacts on the floral community that can hamper NTFP-based livelihoods of the
local community around BMWS & NP.
ii) The Road Report
mentions that apart from forest land, almost 70.42ha of non-forest land would
be acquired affecting 377 civilian and governmental structures (Table 5.17,
Page 85). It is not clear what the
extent of damage to these structures would be.
Further, the assessment does not delve deeper into the livelihood
impacts and possible mitigation plans for families affected by the
project. It mentions that a separate
land acquisition plan would be devised for these aspects and has no concrete
mitigation plans for social impacts.
4.
REVIEW OF ASSESSMENT STUDY FOR THE RAILWAY EXPANSION PROJECT
While the assessment study
(hereafter Railway Report) for railway expansion was informative and detailed,
it suffered from several shortcomings as well.
The authors reviewed it for information on the same parameters –
assessment of taxonomic groups, environmental, and social impacts. It is noteworthy that the railway expansion
will affect not only the BMWS & NP but also the neighbouring Kali Tiger
Reserve in Karnataka State. Therefore, a
project which will fragment the only intact tiger and elephant population in
the north-central Western Ghats will have severe ramifications for wildlife and
biodiversity. The Railway Report,
however, does not stress on the ecological impacts of railway expansion and
instead presents a neutral portrait of the project impacts by emphasizing
uncertain mitigation measures.
4.1
Plants
i) In the section on
vegetation characteristics, it is mentioned that 255 species of flowering
plants were recorded (Page 64), but Appendix 2.1.a. of the Railway Report lists
224 woody trees. The IUCN Red List status
is not provided, and a few common endemic species that occur in the region are
not mentioned in the tree species list.
ii) The floristic survey
results (Page 83) only records seedlings of woody trees but not herbs and
orchids, some of which are rare with restricted distribution in the Western
Ghats (Joshi & Janarthanam 2004).
iii) Plant species are
misspelled or outright erroneous in the Appendix which makes it difficult to
identify the plants that will be impacted.
For example, Euonymus undulatus is misspelled (correct name: Euonymus
angulatus), while Lapisanthes microphylla is an invalid scientific
name as per our knowledge.
iv) Appendix 2.1.a of the
Railway Report mentions 13 plant species (including vulnerable and endemic
species) which are yet to be recorded from Goa.
Three of those species may not occur in the BMWS & NP and need
further scrutiny as to the validity of their inclusion, however, even if they
do occur, it only reveals the importance of the region for plant diversity, and
therefore the region should not be diverted for the railway expansion.
4.2
Insects
i) The Railway Report
follows standardized protocols to document butterfly diversity of the region
but covers a very small area which might not represent all the habitats
affected by the project, a fact acknowledged in the study (Page 87).
ii) The survey was carried
out from April (2013) to May (2014), however, there is no mention of the
duration of data collection, including details on whether surveys were
undertaken every month or a few days every season. This would have a bearing on the findings.
iii) There is no mention
of whether sampling effort was replicated.
This precludes an understanding of how many times a transect was
sampled, and whether the same transects were sampled repeatedly in subsequent
seasons. Quantitative analysis of data
collected with inadequate sampling protocols may lead to incorrect estimates of
insect diversity.
iv) The Railway Report
mentions that the Family Lycaenidae and Hesperiidae were represented by 33 and
18 species, respectively. The number of
species, however, might be under-represented given the difficulty in visual
identification of species belonging to these Families. No effort was made to account for detection
issues in the Railway Report.
v) The Railway Report also
does not provide an assessment on moth diversity. Moths are ecologically important and even
more diverse than butterflies and dragonflies.
At least 418 species of moths of which 116 species are unidentified,
were reported from the north Western Ghats (Shubhalaxmi et al. 2011). Given that the study site is a PA in the
Western Ghats, it is likely to have high moth diversity.
vi) There are
discrepancies in the listing of species in the Railway Report. For example, butterfly species such as Neptis
columella, Doleschallia bisaltide, Actolepis puspa, and
Castalius rosimon which are Schedule I species are left out of the
scheduled species list and the text, with only a passing mention in the
Appendix of the Railway Report (Appendix 2, Page 89).
4.3
Fish
i) The Railway Report
records the presence of 23 fish species, however, a comprehensive study in the
Mhadei sub-basin (which includes BMWS & NP) reported 49 fish species with
18 endemics from the Western Ghats (Atkore 2017; see Appendix IV).
ii) The Railway Report does
not assess potential impacts of the project on fish community structure, even
though studies have found that alteration of stream environment (changes in
water quality and flow alteration) by anthropogenic pressures have negative
influences on fish guild composition (Atkore 2017; Atkore et al. 2020).
4.4
Herpetofauna
i) The Railway Report has
a fairly comprehensive assessment of amphibians and reptiles. It reports key details about the diversity of
herpetofauna, including endemics, however, it only mentions the impact of the
railway-line in causing mortality of reptiles (Page 140), and remains
inconclusive of impacts on amphibians (Page 135).
ii) The survey on
amphibians clearly finds that 13% of endemic Western Ghats species (14 species
out of 24) were found in the project area.
This number is likely higher and points to the sensitivity of the region
for anurans (See Appendix VIII of this paper).
iii) For reptiles, the
Railway Report finds 27 species, which is an underestimate (See Appendix VII of
this paper). The report does not have an
exhaustive assessment of impacts due to the railway expansion on herpetofauna,
reasoning that the study was carried out “during the inactive period of
reptiles (winter) where the intensity of the impact could not be assessed
properly due to their high seasonal activity, secretiveness and less
conspicuousness” (Page 140).
4.5
Birds
i) The Railway Report
mentions that a two-day survey for birds was carried out in September 2014 and
May 2015. It is not clear why a short
survey effort was employed to compile the checklist. The survey enumerates only 35 species, of
which nine were endemic species. This is
an underestimate, compared to the 286 bird species recorded in the BMWS &
NP in a comprehensive checklist (Rahmani et al. 2016; eBird 2017).
ii) Data is collected only
for cavity-nesting birds. This omits
species that do not nest in cavities, but are dependent on trees and vegetation
for nesting and feeding. The reason for
surveying only cavity-nesting birds is not provided. Further, migratory birds are
under-represented in the survey, given that the survey was not carried out
during the migratory season between October–March.
iii) The Railway Report
mentions, “The loss of tree specially >10 and >60cm dbh would impact the
nesting of birds in the proposed project area” (Page 145). Again, this focuses only on cavity-nesting
birds, and undermines the importance of shrubs and undergrowth for passerines
and understorey insectivores, which will also be impacted. Such impacts of the loss and fragmentation of
the forest cannot be mitigated or compensated for, with respect to
ground-nesting and understorey insectivorous birds (Lampila et al. 2005).
iv) The project area
description (Page 19) mentions the state bird of Goa as the Ruby-throated
Yellow Bulbul Pycnonotus dispar.
This is an error. The state bird
of Goa is the Flame-throated Bulbul Pycnonotus gularis, while P. dispar
is a bird found in the forests of Java and Sumatra.
4.6
Mammals
i) The Railway Report
suffers from multiple lacunae such as inadequate sampling effort. Species accumulation curves, which could have
accounted for this limitation, were not generated.
ii) The sampling methods
also do not account for detection issues (i.e., false negatives; Sollmann et
al. 2013). This is especially pertinent
given that a much higher number of mammal species occur in the region, which
find either inconsistent, or no mention in the Railway Report (See Appendix III
of this paper). For example, the
Executive Summary (Page 5–6) mentions 42 mammal species were found using a
literature survey, but the presence of the Bengal Tiger (India’s National
animal) is not explicitly stated.
Appendix 2 of the Railway Report (Page 166) mentions 23 species of
mammals, but does not mention which of those are Schedule I species, even
though the region has 11 Schedule I mammal species. The ecological value of the region may have
been underemphasized due to these inadequate methods as many more mammal species
that occur in the region are likely to have been missed as they were not
accounted for (Hayward et al. 2015).
iii) The description of
the methods is very sparse and limits clear understanding (Page 153). The sampling unit was undefined — signs were
recorded both inside and outside of belt transects. The study description lacks any detail about
statistical methods used to assess species richness or percentage occurrence or
relative abundance, using indirect signs or direct sightings.
iv) Randomly placed
belt-transects used in the Railway Report are not a suitable choice to assess
large and small carnivore species richness and occurrence (Barea-Azcón et al.
2007). Further, signs were recorded
opportunistically from outside of belt transects (Results, Page 153–154), but
no clear analytical framework is provided for this data. Carnivores often tend to move on forest
trails, roads, dry streams therefore a non-random or systematic sampling
approach (within beats or grid cells) would be more appropriate to specifically
assess carnivore occurrence in the study region (Karanth et al. 2011).
v) Camera-traps are one of
the best tools available to assess the occurrence, density, and abundance of
mammals (O’Connell et al. 2011). But,
the Railway Report uses a sparse sampling effort by surveying only 16 sites
(camera-traps malfunctioned in nine of the 25 sites surveyed). In addition, the cameras were placed for less
than six days in most sites. Studies
have found a minimum of 20 to 30 error-free days of camera-deployment are
required for stable estimates of species occurrence (Hamel et al. 2013). The standard duration for density assessment
of large cats in Tiger Reserves and PAs of India is 25 days (with a closure
period of 45–60 days). Therefore, a
sampling duration of less than six days used in the Railway Report translates
to poor data collection, which eventually affects any ecological inferences
derived from such studies (Burton et al. 2015).
vi) The camera-trapping
protocols lacks any detail about the camera models used, mode of deployment,
camera-settings, and study design (Meek et al. 2014).
vii) Table 2.8.1 (Page
154) reports the species Viverra zibetha (Large Indian civet) which is
not found in the Western Ghats, but in northeastern India. The table also mentions the occurrence of an otter
species, Lutra lutra, the Eurasian Otter, which has not been recorded
from the region. The Railway Report
provides no evidence of its presence in the form of photographs. Two other species of otters which have been
recorded and photographed in the region, the Asian Small-clawed Otter and the
Smooth-coated Otter are not mentioned (Punjabi et al. 2014; Krupa et al.
2017). Page 161 of the Railway Report
has erroneously labelled Wild Pig Sus scrofa as Indian Porcupine Hystrix
indica.
viii) Appendix 2 in the
Railway Report (Page 166) has incorrect coding for species: Langur and Bonnet
Macaque are listed as herbivores (when they are actually primates); Asian Palm
Civet is coded as a carnivore, but the Small Indian Civet, Brown Palm Civet,
and Stripe-necked Mongoose are incorrectly coded as herbivores; the otter and
Indian Pangolin are coded as large mammals, but the Asiatic Wild Dog, which is
larger in size is coded as a small mammal.
This reveals a naive understanding of mammals and the impacts that railway
expansion could have on low-density species such as carnivores.
4.7
Land-use
i) The land-use land-cover
map was derived from classification of single date satellite data, acquired in
April 2013. Since the project area
supports different types of vegetation which have variation in spectral
signatures during different seasons, an ideal mapping exercise should have
considered seasonal data, for at least two different seasons within one year.
ii) Out of six effective
bands of Landsat and eight for vegetation discrimination, only four bands have
been used for classification. This
essentially leaves out the details of land-cover class categories that are
clearly identified by the other two short-wave infra-red bands. These two short-wave IR bands demarcate the
response of vegetation to moisture stress, and thus improve the classification
of the forest types (Ferreira et al. 2016).
iii) The reasoning behind
the number of sampling points used for each land-cover category is not
clear. It is stated that unsupervised
classification, which yielded 15 classes, was used as a basis for ordering the
landscape into distinct units. It is
unclear, however, if these ‘distinct units’ were further assigned land-cover
classes on the basis of any reference map.
A reference map could have informed the locations where ground truth
data was necessary for ascertaining land-use types.
iv) The exact methodology
for land-cover classification, parametric (maximum likelihood, minimum distance
to means), or non-parametric (support vector machines or any other) has not
been mentioned. This prohibits a nuanced
understanding of the method of classification for a forest complex.
v) Ancillary data such as
topographical information from an elevation model have not been utilized for
assessments. A simple elevation profile
of the proposed railway route indicates an elevation range of 80–500 m. In a high elevation area with varying
gradients, the topography of the land determines much of the vegetation
assemblages, and this could be important information to include in the
classification process. The importance
of topographic information for vegetation mapping is a widely accepted
methodology (Das et al. 2015; Roy et al. 2015) and earlier work in the Eastern
Ghats region has used topographic information effectively to this end (Balaguru
et al. 2003).
vi) The basis for accuracy
assessment has not been mentioned. An
overall accuracy of 88% is indicated, but no reference map seems to have been
used for calculation. The report also
does not mention the percentage of samples used for training and testing the
classification, which is a standard accuracy assessment procedure.
4.8
Water
i) Water pollution is a
major concern during the construction as well as during the operation phase.
Water pollution analysis, however, was minimal with no monitoring of pollutants
done for polycyclic aromatic hydrocarbons (PAHs) and heavy metals because of
the existing railway-line, despite high concentrations being often reported in
waterways bisected, or bordered by railways (Wiłkomirski et al. 2011;
Wiłkomirski et al. 2012; Levengood et al. 2015).
ii) Furthermore, Escherichia
coli bacterial contamination was reported in all sampled streams,
indicating faecal contamination, which may be attributed to waste disposal from
passing trains. The total coliform count
ranged from 221/100mL to 542/100mL, while the safe threshold value is 100
count/100mL. The increased risk of
coliform contamination resulting from the railway expansion is a severe threat,
as many streams that cross the tracks harbour sensitive wildlife, and also
supply water to villages downstream for drinking and farming.
4.9
Air
i) No air quality
monitoring was performed to provide baseline levels or to establish the risk of
railway expansion in this region. The
Railway Report assumes that engines will be electrified; however, if existing
diesel engines are used then the doubling would increase the amount of
pollutants associated with combustion and diesel emissions.
ii) The main constituents
of diesel engine exhaust emissions are Carbon (CO, CO₂), Nitrogen (N), Nitrogen
Oxides (NOx), Sulphur Oxides (SOx), Hydrocarbons (HC), Methane (CH4),
Non-Methane Volatile Organic Compounds (NMVOC), PAHs, and particulate matter
(PM) (Borda-de-Água et al. 2017).
Monitoring of the current pollutant levels should have been performed at
least twice a year to avoid data bias due to seasonal variation, although
quarterly (or even monthly) sampling events could have been employed
(Jayamurugan et al. 2013; Manju et al. 2018).
4.10
Soil
i) Chemical properties of
soil and baseline levels of soil pollution were not established during sampling
and analysis. Soil and plants
surrounding the railway lines should be monitored for organic and inorganic
compound contamination, resulting mostly from used lubricant oils and condenser
fluids, the transportation of oil derivatives, metal ores and other chemicals,
as well as from application of herbicides and other treatments to the train
vehicles. These pollutants, however,
were not considered in this assessment.
ii) PAHs, heavy metals,
oil-derived HC, and to some extent, polychlorinated biphenyls (PCBs) should be
monitored in soils, with risks comprehensively assessed as they exhibit
toxicity, long-term stability and a cumulative effect in the environment (Wiłkomirski
et al. 2011; Wiłkomirski et al. 2012; Levengood et al. 2015; Pereira et al.
2015). PAHs are carcinogenic and
mutagenic to living organisms (IARC 1989).
The main source of PAHs in railway areas are machine grease, fuel oils
and transformers oils. Heavy metals
(such as Pb, Cd, Cu, Zn, Hg, Fe, Co, Cr, Mo) originate mainly from material
abrasion and fuel combustion in diesel and electric locomotives, therefore the
railway expansion will lead to further heavy metal contamination in soils.
4.11
Social Impacts
i) The Railway Report’s
socio-economic survey of 60 families conducted in four villages does not report
the total number of affected families, demography and livelihood patterns of
concerned villages. The sampling strategy
and the criteria for selection of households is unclear. The questionnaire was focussed on the
perception of transport models by local communities. The questionnaire did not have open-ended,
non-leading questions to bring out local concerns towards the project, and
possible impacts on their livelihood and environment. Instead, it addressed questions such as
preferred mode of transport, where 90% of the respondents listed trains.
ii) The Railway Report
mentions a public consultation meeting regarding the railway expansion project
that occurred in June 2016 at Kulem Panchayat (Hindi: Village Council) office
(Page 190). The Kulem Panchayat raised concerns about the impact of the project
on the Dudhsagar waterfall which contributes revenue from tourists to the local
economy, availability of medicinal plants and disturbance to the temple close
to Sonalium Station (Page 191). The
consultation meeting was attended by only 14 members, most of whom were
panchayat office bearers and members of the biodiversity committee, but not by the
general public who would be affected by such developmental projects. As this meeting took place in 2016, before
the Railway Report was published (in 2017), it is unclear whether a public
hearing took place after the report was published. This suggests that the affected public is
unaware of the damage the expansion may bring to their livelihoods.
iii) The Railway Report
mentions that NTFPs and medicinal plants from the forest area were important
for local use (Pages 169–171), but the specific impacts of the railway
expansion on such NTFP and medicinal plant species were not assessed. Datar & Lakshminarasimhan (2011) reported
that local communities around BMWS were dependent on the forest for wild edible
mushrooms, fruits, herbal medicinal plants, and specific plants for cultural
use. This indicates that it is important
to assess the impact of the proposed project on NTFP collection.
iv) The Railway Report
finds that existing faecal contamination in the streams near to the railway
tracks and the level of contamination is already 2–5 times the prescribed
limit. Waste generation due to
construction debris within the forest can further pollute soil and water
resources in this sensitive region, thereby also affecting human
communities. Increased waste dumping by
railway passengers near villages can attract wildlife to these villages, which
can result in human-wildlife conflict scenarios.
5.
REVIEW OF THE 400kV TRANSMISSION LINE
The
transmission line project did not have the assessment study in the public
domain and therefore this limited our review to aspects of this project for
which information was available in the public domain on the Parivesh
portal. The key concerns with the
transmission line project are discussed here.
i)
The construction of new power lines in forest areas of high conservation value
should be avoided (Eldegard et al. 2015).
The transmission line project passes through a PA (11.54 ha inside PA)
and the total forest land required for the project is 48.3 ha (almost 50 ha,
for which an EIA is necessary from a socio-ecological point of view). The minutes of the meeting of the Goa State
Board for Wildlife held on 02 December 2019 mentions that “the Biodiversity
Impact Assessment studies and Biodiversity Management Plan has been prepared by
ERM India Pvt. Ltd, Gurgaon has been submitted”. The same, however, is not available in the
public domain to allow a clear assessment of projected impacts.
ii)
The detailed project report that is available for the transmission line makes
contradictory statements about the location of the transmission line in the
BMWS & NP. It first states that
2.51km of the transmission line is within the NP, clearing an area of 11.54ha
(Table 1, Page 2, Detailed Project Report).
Subsequently, when justifying the reason for choosing between
alternative routes of the transmission line, it states that the chosen route
fully avoids the NP. These statements
severely weaken the report and hinder an effective assessment of the impacts of
the transmission line, which already lacks sufficient public scrutiny. An inspection report by the forest department
indicates that over 4,146 trees and 985 cane clumps in the PA are to be cut for
the project.
iii)
The project proponent claims that “transmission line projects are environment
friendly and do not involve any disposal of solid effluents and hazardous
substances in land, air and water.
Moreover, forest area trees are felled below each conductor to
facilitate stringing. On completion of
construction only one strip is maintained for O & M purpose. Therefore, the actual loss of forest is
restricted to some selected areas only.”
These statements do not recognize the larger effects of the transmission
line on birds and volant mammals such as bats and gliding squirrels, or on arboreal
species such as the Slender Loris, Giant Squirrel, Bonnet Macaque, and Grey
Langur. For example, due to the absence
of tree cover along transmission lines, arboreal mammals such as Lorises are
forced to use electric wires of power lines to cross, causing mortality due to
electrocution (Raman 2011).
iv)
The project requires a clearance for 35 years, during which there will be
regular cutting below the transmission line.
This is especially concerning given that the project cuts through the
PA, so the effects of this project are long-term.
v)
The statement “the actual loss of forest is restricted to some selected areas
only” fails to take into account existing evidence that power lines are linear
intrusions that prevent animal movement, fragment communities of small mammals
(Goosem & Marsh 1997), and cause mortality due to electrocution and
collision (Jenkins et al. 2011; Rioux et al. 2013; Loss et al. 2014; Uddin
2017). Large mammals have also been
electocuted due to sagging power lines (Raman 2011). The area underlying the proposed transmission
line currently (i.e., without the construction of the power line) offers low
resistance to large mammal movement, indicating that the area is important for
animal movement (Jayadevan et al. 2020; https://indiaunderconstruction.com). In their paper, Jayadevan et al. (2020)
recommend avoidance of new infrastructure in areas that currently pose a low
resistance to movement.
vi)
Transmission lines have several impacts on birds. Studies have shown that birds avoid areas
between 0.25 and 0.6 km of transmission lines (Dunkin et al. 2009; Gillan et
al. 2013). Transmission lines cause bird
mortality due to electrocution and collision (Uddin 2017; Biasotto & Kindel
2018). For example, many birds use
structures of transmission lines as a perch, which often leads to electrocution
(Biasotto & Kindel 2018). The
clearing of trees for the transmission line affects the movement and nesting
success of birds (Biasotto & Kindel 2018).
vii)
The conservation value document uploaded by the wildlife warden details the
damaging effects of the project. The
document, however, concludes that the movement of faunal species will not be
affected by the project, and the loss of trees can be compensated via
afforestation. This is inaccurate, as
transmission lines would impact movement of fauna, in addition to other
deleterious impacts including mortality, as we detail above. Further, compensatory afforestation at a
different site does not ameliorate any of the ecological impacts within the PA,
as mentioned in the document.
6. DISCUSSION
We
argue that mitigation measures proposed in the Road Report, Railway Report, and
documents for the transmission line are inadequate and will not alleviate
serious damage to the BMWS & NP or ecologically-sensitive regions around
the PAs. We have explained this in
detail in the following sections.
6.1 INADEQUACY OF MITIGATION MEASURES FOR NH-4A
i)
For the mitigation measures, the Road Report merely notes that “Mitigation of
man versus animal conflict is going to be the important issue that will
threaten wildlife in Sanctuary area” (Page 97, Section 6.3.9 (i)). There are, however, no mitigation measures
recommended to reduce the conflict created by road expansion. An acknowledgement of an important socio-economic
and environmental problem will not equip the Goa Forest Department, National
Highways Authority of India, or the Public Works Department of Goa to
effectively manage the problem created by road expansion without detailed
mitigation plans.
ii)
For terrestrial fauna, the Road Report states that no impact on the wildlife is
anticipated and hence does not outline any mitigation measures (Page 97,
Section 6.3.9 (II)). Given that nearly
32ha of forest land will be diverted for the project, there is likely to be an
impact on wildlife. There is growing
scientific evidence demonstrating that building new roads and their upgradation
or expansion has serious impacts on wildlife in protected areas. For example, Garriga et al. (2012) found a
total of 2,013 wildlife mortalities on roads within protected areas of
Catalonia, of which 267 were mammals (13.3%), 253 birds (12.6%), 245 reptiles
(12.2%), and 1,248 amphibians (62.0%). A
total of 85 different species were affected across all taxa due to roads within
PAs over just two seasons, Spring and Autumn, in one year.
iii)
As a measure to mitigate vegetation and habitat loss, the Road Report mentions
that “an avenue plantation programme shall be promptly adopted to restore and
further enrich the loss of vegetation” (Page 96, Section 6.3.9 (i)). Such measures may increase green cover, but
they do not mitigate the impacts of road construction on vegetation or
wildlife. Instead, it also puts people
at risk due to the increased likelihood of vehicular collision with mammals
(Case 1978; Jaren et al. 1991; Putman 1997; Cain et al. 2003).
iv)
The Road Report proposes “periodic maintenance of drains to check
scouring of soil” to decrease soil erosion (Page 92, Section 6.3.5). Soil erosion is expected to be higher in
tropical forests, such as BMWS & NP, due to its wet climatic conditions and
steep terrain (Sidle et al. 2006; Sidle & Zeigler 2012). Deposition of eroded soil into rivers at an
increased rate is responsible for increasing turbidity and temperature of the
water, reducing the amount of dissolved oxygen and changing existing flow
regimes, while accelerating eutrophication (Beevers et al. 2012; Douven &
Buurman 2013). The proposed clearing of
land for the development of the road is likely to make cut sections highly
susceptible to soil erosion. Drainage
structures and culverts are essential to allow better above-ground water
drainage, and prevent drastic changes to the hydrology of the landscape and
decrease flooding along the road during monsoon seasons (Sidle et al. 2006;
Laurance et al. 2009). No site-specific
hydrological survey has been carried out to arrive at the optimal number of
culverts and bridges, and their spatial placement.
v)
Although the Road Report aims to reduce the impact of the developmental project
in the “direct path” of the roadworks, it is pertinent to understand that the
impacts of road construction are rarely limited to the direct path. Environmental impacts of roads extend beyond
the direct impacts of construction and tree clearing, to indirect impacts
because of increased human access and vehicular traffic. This includes, but is not limited to, air,
water, and noise pollution, disturbance effects, fragmentation due to edge
effects, and hindrances to migratory corridors (Alamgir et al. 2017).
6.2 THE IMPACT OF ROADS
We
further expand on biotic and abiotic impacts of roads here, for which no
mitigation measures have been suggested.
i)
Roads compound the impacts of natural disasters
Constructing roads in
hilly and mountainous terrain increases the risk of natural disasters such as
landslides and flooding (Sidle et al. 2006; Larsen & Torres-Sánchez 1997;
Larsen & Parks 1998). There is no
information on the susceptibility of the proposed site to extreme weather
events in the EIA. Such dissemination of
information regarding the socio-economic and environmental risks involved in
the project is critical to the decision of investors, decision-makers and
taxpayers, whose money is being utilized for the project. Road projects that pass through forested
areas and lack proper planning can lead to major cost overruns, corruption, and
damage to the environment (Trombulak & Frissell 2000; Alamgir et al. 2017)
ii)
Roads are a cause for wildlife mortality (roadkills)
Enabled by the expansion of
the highway, an increase in vehicular traffic in the area can be expected. This will likely increase the rates of
wildlife-vehicle collisions, impacting species of most terrestrial fauna. A study from Mudumalai Tiger Reserve found
road mortality of 40 animal species, including amphibians, reptiles, birds, and
mammals (Baskaran & Boominathan 2010).
Additionally, animals that are slow-moving or burrowing, such as
freshwater turtles, amphibians, snakes, and soil-living fauna, get killed
during road construction. The impacts of
earthwork and annual maintenance operations on terrestrial fauna are usually
overlooked (Clevenger et al. 2003; Fahrig et al. 1995; Trombulak & Frissell
2000; Goosem et al. 2010).
iii)
Roads are barriers to wildlife movement, and cause habitat fragmentation
For many species,
particularly in the Western Ghats, the expansion of the NH-4A is an additional
fragmentation of an already fragmented habitat (Nayak et al. 2020). The resistance to potential large mammal
movement posed by the existing NH-4A is higher than the median resistance to
mammal movement in the Western Ghats (Jayadevan et al. 2020;
https://indiaunderconstruction.com).
Expansion of the road can, thus, lead to an increase in the resistance
posed to movement, and lead to increased isolation between forest patches on
either side of the road.
Subdivision of remnant
forest patches due to various linear intrusions such as highways and roads
causes “internal fragmentation” (Goosem 1997; Goosem 2007). Such internal fragmentation with wide,
cleared roads and their edges, physical barriers such as fences and crash
barriers, cuttings, fill batters, and culverts with drop structures, could be a
serious threat to movement of wildlife and lead to increased negative
human-wildlife interactions (Goosem et al. 2010). For example, many animals in tropical forests
avoid even narrow linear clearings (< 30m wide; Holderegger & Di Giulio
2010; Laurance et al. 2009). Increased
traffic and continuous vehicular movement can stress the animals or make
species alter their behaviour in the vicinity of roads (Trombulak &
Frissell 2000). While certain species
such as macaques are attracted to roads for scrap food from travellers (a
potential ecological trap), species such as Elephants have been observed to
avoid roads and highways due to associated risks, or suffer mortality from
collisions (Blake et al. 2008).
Behavioural avoidance of the road may also be exhibited by animals that
can fly over the width of the road (e.g., birds and bats), due to the noise,
pollution, and risk of crossing (Laurance et al. 2009).
The problem of
fragmentation by roads is particularly acute for canopy dwelling species that
use closed-canopy structures to move and do not generally use the ground to
cross. In the absence of tree cover,
tree-dwelling animals are forced to either use the ground or cross using power
lines, which can lead to mortality due to vehicular collisions or
electrocution. This is especially the
case for primates, arboreal rodents, and some carnivores (Radhakrishna &
Singh 2002; Raman 2011).
iv)
Roads affect the genetic diversity of animals
Decreased movement of
animals across roads leads to decreased genetic variation, due to reduced
genetic exchange between populations.
For example, studies from India show that roads negatively affect tiger
connectivity (Joshi et al. 2013; Dutta et al. 2018; Thatte et al. 2018). Such impacts can be seen after just a few
generations in populations of large mammals that have been separated by newly
built roads and highways (Holderegger & Di Giulio 2010).
v)
Roads affect biodiversity due to increased noise pollution
Although monitoring of
noise quality levels created by the existing highway was carried out at eight
sites designated as commercial, industrial and residential, there was no
monitoring carried out on existing highway stretches within the protected
area. Noise quality levels were found to
be “within the limits” for commercial and industrial categories but “exceed the
limits” in the residential category. Noise pollution associated with roads has been
shown to decrease reproductive capacity in bird and amphibian species, as well
as in mammals such as Tigers (Kerley et al. 2002; Hoskin & Goosem 2010; Qin
et al. 2014; Laurance 2015), with impacts seen at the community level as well
(Francis et al. 2009; Slabbekoorn & Halfwerk 2009).
vi)
Roads lead to increased human accessibility
Roads passing through
forested areas increase human accessibility and can increase movement,
settlement and human activity in frontier forest areas. This has manifold repercussions including
forest fires, waste disposal and pollution, illegal timber harvest, poaching
and hunting (Alamgir et al. 2017). Studies
from protected areas in developing economies show that road expansion and
improved accessibility to the market can result in expansion of agricultural
and livestock frontiers with reduction in nearby forest areas of the protected
area (Ratner et al. 2007; Lama & Job 2014; Phaipasith & Castella 2017;
Walelign et al. 2019). Conversion from
subsistence agriculture to cash crops, emergence of commercial service
economies such as mass tourism resulted in transition from a low-impact economy
to a high-impact one (Walelign et al. 2019).
Local socio-economic inequality also increased after road-expansion
(Ratner et al. 2007). In the long run,
the negative impact on the forest, waste generation and excessive use of
agro-chemicals resulted in lesser availability of clean water, reduced soil
fertility and local extinction of NTFP species (Phaipasith & Castella
2017). This also affected local
governance systems negatively and people often could not revert to their
subsistence economies which were relatively sustainable (Lama & Job 2014).
vii)
Roads as a cause for habitat loss and degradation
During the construction
and maintenance of roads and highways, habitat loss and degradation is observed
due to direct clearing of vegetation, dumping of excavated earth and materials,
regular usage of access roads by heavy machinery, and construction of labour
camps. Within tropical forests,
disturbance from roads due to fluctuations in light, temperature and humidity,
increased mortality of trees beside roads, and spread of exotic species to a
width of least 100m from the road (Laurance et al. 2009). Thus, “each kilometre of road directly and
detrimentally affects at least 10 ha of habitat”, and the impacts may persist
for decades (Laurance et al. 2009; Raman 2011).
viii)
Roads as corridors for invasive species
Roads have been found to
be a major factor in the spread of invasive flora and fauna into forests
(Mortensen et al. 2009; Meunier & Lavoie 2012). These invasive species can use the edge
habitats along the road and invade forests by secondary wind dispersal, that
would have otherwise been inaccessible (Kowarik & von der Lippe 2011).
6.3
THE IMPACT OF RAILWAY-LINE DOUBLING AND INADEQUACY OF MITIGATION
i)
Air quality
No potential impacts on
air quality were studied, as the railway line between Castlerock and Kulem was
assumed to be electric. If the trains in
the proposed stretches run on traditional diesel engines, increased locomotive
traffic due to the doubling of the railway line will lead to an increase in
harmful exhaust components. The main
pollutants from diesel locomotives are Carbon Dioxide (CO2), Carbon Monoxide
(CO), Sulphur Dioxide (SO2), Nitrous Oxide (N2O), particulate matter (PM),
hydrocarbons (HC), among others. Many of
these pollutants are carcinogenic and responsible for health and environmental
impacts (Lucas et al. 2017).
The report suggests
monitoring of air quality and minimizing air pollution due to dust particles,
vehicular and locomotive emissions, during the construction and operational
phase. Although necessary, such general
recommendations on controlling impacts on air quality during the construction
phase will minimally help in reducing pollution as the project will take three
years to construct and the operational impacts will be near permanent. Abrasion of brakes, wheels, dust, mineral
transport will all still produce PM emissions even if electric locomotives are
used (Levengood et al. 2015). No amount
of mitigation will compensate for the long-term impacts of air pollution due to
the proposed expansion.
ii)
Sound (Noise pollution)
The noise levels at various
regions within the areas of the proposed project were already noted to be above
the permissible level of 91dB, posing a serious threat from noise
pollution. Anthropogenic noise can
affect acoustic communication among bird species that use calls and songs for a
variety of functions such as attracting mates and defending territories
(Collins 2004; Marler 2004). Noise
emission from railways has also been documented to reduce the density and
nesting behaviour of birds, with nests that are farther away from railway lines
being more successful (Mundahl et al. 2013).
To reduce noise pollution,
the Railway Report recommends switching to electric engines, planting native
tree species along the railway line and building sound barriers on both sides
of the track, particularly within the biodiversity-rich Kali Tiger Reserve
(from Castlerock station – Goa border) and BMWS & NP. All of these three recommendations, however,
have serious drawbacks which the report has overlooked.
a. Switching to electric engines will not greatly reduce
noise pollution. This is because, at a
speed of 30–200 km/h (the speed at which most trains will be travelling between
stations), all trains, including the electric trains, produce a “rolling noise”
which is the dominant source of noise pollution (Clausen et al. 2012).
b. Recovering vegetation beside roads and railways is known
to attract wildlife and increase their vulnerability to get killed by moving
vehicles (Case 1978; Jaren et al. 1991; Putman 1997; Cain et al. 2003).
c. Sound barriers will further intensify the impacts of
forest fragmentation caused due to railways.
While the size and structure of sound barriers are not mentioned in the
report, they are usually artificially built, vertical walls of a solid
structure, which blocks the noise created by moving trains. While this could be a reasonable mitigation
measure for railway lines that pass through human habitat, it will have
detrimental ecological impacts inside a forest ecosystem. Sound barriers can cause various negative
impacts on wildlife, particularly through isolation of populations (Bank et al.
2002). Given that the minimum height of
such barriers is as high as the train, and with electric lines proposed to be
running on top of the railway, it would make it impossible for any terrestrial
species to freely move to the other side of the track and will be a death trap
for wildlife trapped between the barriers.
iii)
Water quality
The
Railway Report states that the current water quality in streams along existing
railway track is pristine (Bureau of Indian Standards 2012), but with harmful
levels of bacteria Escherichia coli in all streams (221 to 542 per
100mL), it indicates widespread faecal contamination of waterbodies mostly due
to exisiting train traffic (threshold is 100 per 100mL). Creation of new railway embankments for the
proposed double gauging will further lead to vegetation loss, soil compression
and changes in water drainage, thus increasing runoff, promoting erosion of
topsoil and increasing water turbidity (Ferrell & Lautala 2010; Chen et al.
2015). Turbid water has been found to
affect the diversity and abundance of aquatic wildlife communities such as
odonates and freshwater fish (Luce & Mountain 2002).
The Railway Report
mentions that the new railway coaches will be fitted with bio-toilets, hence
reducing the likelihood of E. coli infiltrating streams along the
railway route. Construction of dykes and
retaining walls along the railway line to restrict the movement of sediments
during the construction phase has been recommended. While this may address sediment runoff, it
may indirectly inhibit animal movement, adding to the effects of tree clearing,
noise, and train movement.
iv)
Biodiversity
The major focus of the
studies appears to be to create baseline information on species diversity and
abundance, rather than to explicitly study the impact of the proposed expansion
on biodiversity. The Railway Report only
cursorily mentions that animal movement will be impacted by the doubling of the
railway line (Chapter 18, Page 207) and does not address long-term impacts to
landscape connectivity that all the taxa under study face from the proposed
expansion of the railway line. There is
strong evidence of the negative impacts of railway lines on biodiversity.
Railway lines have been
shown to be barriers to movement for large mammals such as the tiger (Dutta et
al. 2018). The current railway line
between Kulem and Castlerock poses a high degree of resistance to large mammal
movement (Jayadevan et al. 2020).
Doubling of the railway track will lead to a higher frequency of trains,
and further increase resistance to movement.
This can isolate the forest patches on either side of the railway
line. In addition to its impacts on
movement, noise and vibrations from railways affect insects, amphibians, and
birds. Further, the availability of food
(solid food waste; carcases of dead animals) and vegetation along the railway
edges attracts reptiles, few species of birds, and several mammals acting as an
ecological trap and leading to higher mortality due to collision with trains
(Lucas et al. 2017).
The mitigation measures
suggested in the Railway Report are very general. The suggestion of the creation of
‘biodiversity parks’ for conserving birds and mammals is not compensatory, when
the protected area, which is a biodiversity-rich region, will be
fragmented. For aquatic life, it is
suggested that railways should adopt the ‘best construction procedures’ to
reduce turbidity, siltation, etc., but what these procedures comprise of is
unexplained.
The Railway Report
highlights cases of Gaur and Sambar being hit by trains on the existing single
track, reaffirming that the doubling of the railway line will lead to increased
risk of accidental collisions with wildlife.
Although the report identifies 42 animal-crossing points for mammals, a
bare minimum of four animal underpasses are finalized at Ch 32/200, Ch 41/100,
Ch 45/500, Ch 49/500 (RVNL Letter No.PlU/UBLllLN654 dated 06.10.2018 to deputy
forest officer). The report suggests
many other mitigation measures to be followed (Pages 207–208), but such
mitigation measures are undetailed, and without strong supervision during
implementation have poor application in practice.
6.4
INADEQUATE MITIGATION MEASURES FOR THE TRANSMISSION LINE
i) On the subject of
mitigation measures for the transmission line, the inspection report of the
transmission line mentions only that “the user agency has agreed to cut minimum
trees requirements and to adopt wildlife-friendly mitigation measures.” It adds that “trees listed for felling under
this project will be compensated in the long term through the proposed
compensatory afforestation programme covering double the degraded forest land.” It is not clear how ‘minimum tree cutting’
will be calculated or enforced. No
details are provided on where and when the compensatory afforestation will be
executed. Further, without an impact
assessment of the transmission line, it is not clear what ‘wildlife-friendly
mitigation measures’ will be implemented.
ii) The inspection report
fails to take into account the ecological impacts of the transmission line as
we have detailed in this paper (Section 5).
A background paper for the National Board for Wildlife (Raman 2011)
recommends that the first priority for power lines in forests should be
prevention, followed by re-alignment.
The third option of a mitigation measure is suggested only where the
first two have been comprehensively considered and ruled out with sufficient
justification (Raman 2011). In case a
transmission line passes through a biodiverse region, recommended mitigation
measures for transmission lines include insulators on wires to avoid bird
electrocution, placing of perch deterrents on cross-arms and poles and using
large line-markers on earth wires to increase their visibility during the day
and night, thus avoiding collisions by birds and volant mammals (WII
2016). But neither of these are
considered as mitigation measures for this project.
7.
CONCLUSION
Any major infrastructure
projects should be avoided within PAs, unless there are exceptional
circumstances that will clearly show forest diversion will benefit wildlife (as
per the WPA, 1972). Utmost importance
should be given to all environmental and ecological impacts of any project, and
as per the background paper of the National Board for Wildlife itself,
ecologically-harmful projects should be avoided. In the present case, there is not one, but
three large projects which are planned in this ecologically-sensitive
region. It is noteworthy that the
Western Ghats is a designated Natural World Heritage Site by UNESCO. The cumulative impacts of these three
projects may change the entire ecology of the BWWS & NP, as well as the
neighbouring Kali Tiger Reserve, and will result in irreparable damage to its
fragile environment. Further, such
damage will impact the quality of human life within and near the PA. Multiple projects also call for an in-depth
investigation into cumulative impacts on the PA. Cumulative impact studies have been considered
mandatory in many countries (Braid et al. 1985), and are implemented rigorously
for their added value in understanding irreversible changes to existing natural
systems (Xue et al. 2004).
It is pertinent to note
that two of these projects (NH-4A and transmission line) were awarded wildlife
clearances in the 57th meeting of the Standing Committee of the
NBWL, held on 7 April 2020 through a video conference, which is unlikely to
have had critical evaluation. Our review
details how the EIAs and assessments for these projects are considerably weak,
and evidently overlooked by the highest statutory authority that is mandated to
protect wildlife in the country.
Socially- and environmentally-just development is important, but none of
these projects provide any benefit to wildlife or the environment in the BMWS
& NP. Environmental costs and
mitigation measures are not comprehensively assessed in the EIAs and assessment
studies. Information on the land area
for compensation, overseeing agencies for mitigation measures, monitoring and
penalties for non-compliance are also not laid out in detail.
Faulty EIAs and other
assessment studies continue to be condoned by successive appraisal boards and
governments, with a lack of due process.
Such practices consider environmental concerns as a burden on
development, rather than a process that guides sustainable development, which
should, therefore, be strengthened. This
further weakens socio-ecological governance in a country which is ranked a 168
(out of 180 countries) in the Environmental Performance Index (Wendling et al.
2020). Considerable opportunities exist
to improve the EIA and assessment process in India (Paliwal 2006). Incentivising post-clearance monitoring and
evaluation is vital (Duflo et al. 2013); however, a rational screening process
which fortifies existing legislation and avoids forest diversion proposals in
protected areas at the outset itself is most necessary (Rajaram & Das
2011).
For figure
& images - - click here
REFERENCES
Abdel-Latif, N.M. & I.A. Saleh (2012). Heavy metals
contamination in roadside dust along major roads and correlation with
urbanization activities in Cairo, Egypt. Journal of American Science
8(6): 379–389.
Aengals, R., V.M. Sathish Kumar, M.J. Palot & S.R. Ganesh
(2018). A
checklist of reptiles of India (Version 3.0). Zoological Survey of India,
Kolkata, India, 35pp.
Alamgir, M., M.J. Campbell, S. Sloan, M. Goosem, G.R.
Clements, M.I. Mahmoud & W.F. Laurance (2017). Economic, socio-political and
environmental risks of road development in the tropics. Current Biology 27:
1130–1140. https://doi.org/10.1016/j.cub.2017.08.067
Annandale, N. (1919). The fauna of certain small streams
in the Bombay presidency. Records of Indian Museum 16: 109–161.
Atkore, V. (2017). Drivers of fish diversity and
turnover across multiple spatial scales: Implications for conservation in the
Western Ghats, India. PhD Thesis. Manipal University, Ashoka Trust for Research
in Ecology and the Environment (ATREE), xvii+168pp.
Atkore, V., N. Kelkar, S. Badiger, K. Shanker & J.
Krishnaswamy (2020). Multiscale investigation of water chemistry effects on fish
guild species richness in regulated and nonregulated rivers of India’s Western
Ghats: implications for restoration. Transactions of the American Fisheries
Society 149(3): 298–319. https://doi.org/10.1002/tafs.10230
Baidya, P. (2020). A preliminary checklist of ants from
Bhagwan Mahavir Wildlife Sanctuary and National Park, Goa (submitted to the Goa
Forest Department). Centre for Ecological Sciences, Indian Institute of
Sciences, Bengaluru, India, 3pp.
Balaguru, B., S.J. Britto, N. Nagamurugan, D. Natarajan, S.
Soosairaj, S. Ravipaul & D.I. Arockiasamy (2003). Vegetation mapping and
slope characteristics in Shervaryan Hills, Eastern Ghats using remote sensing
and GIS. Current Science 85(5): 645–653. https://doi.org/doi:10.2307/24109105
Bastawade, D.B. & M. Borkar (2008). Arachnida: (Orders
Scorpiones, Uropygi, Amblypygi, Aranae and Phalangida), pp. 211–242. In: Fauna
of Goa. [State Fauna Series 16.] Zoological Survey of India, Kolkata,
531pp.
Bank, F.G., C.L. Irwin, G.L. Evink, M.E. Gray, S. Hagood,
J.R. Kinar, A. Levy, D. Paulson, B. Ruediger, R.M. Sauvajot, D.J. Scott &
P. White (2002). Wildlife Habitat Connectivity Across European Highway (Vol. 2). US
Department of Transportation, Federal Highway Administration, Office of
International Programs, Washington, DC, USA, 47pp.
Barea-Azcón, J.M., E. Virgós, E. Ballesteros-Duperón, M.
Moleón & M. Chirosa (2007). Surveying carnivores at large spatial scales: a
comparison of four broad-applied methods. Biodiversity and Conservation
16: 1213–1230. https://doi.org/10.1007/s10531-006-9114-x
Baskaran, N. & D. Boominathan (2010). Road kill of animals by
highway traffic in the tropical forests of Mudumalai Tiger Reserve, southern
India. Journal of Threatened Taxa 2(3): 753–759. https://doi.org/10.11609/JoTT.o2101.753-9
Beevers, L., W. Douven, H. Lazuardi & H. Verheij (2012). Cumulative impacts of
road developments in floodplains. Transportation Research Part D: Transport
and Environment 17(5): 398–404. https://doi.org/10.1016/j.trd.2012.02.005
Bennett, V.J. (2017). Effects of road density and pattern
on the conservation of species and biodiversity. Current Landscape Ecology
Reports 2: 1–11. https://doi.org/10.1007/s40823-017-0020-6
Biasotto, L.D. & A. Kindel (2018). Power lines and impacts
on biodiversity: A systematic review. Environmental Impact Assessment Review
71: 110–119. https://doi.org/10.1016/j.eiar.2018.04.010
Biju, S.D., S. Garg, K.V. Gururaja, Y.S. Shouche & S.A.
Walujkar (2014a). DNA barcoding reveals unprecedented diversity in dancing
frogs of India (Micrixalidae, Micrixalus): a taxonomic revision with
description of 14 new species. Ceylon Journal of Sciences (Biological
Sciences) 43(1): 1–87. https://doi.org/10.4038/cjsbs.v43i1.6850
Biju, S.D., S. Garg, S. Mahony, N. Wijayathilaka, G.
Senevirathne & M. Meegaskumbura (2014b). DNA barcoding, phylogeny and
systematics of golden-backed frogs (Hylarana, Ranidae) of the Western
Ghats-Sri Lanka biodiversity hotspot, with the description of seven new
species. Contributions to Zoology 83(4): 269–335. https://doi.org/https://doi.org/10.1163/18759866-08304004
Bureau of Indian Standards (2012). Indian Standard Drinking
Water - Specification (Second Revision). Bureau of Indian Standards, Drinking
Water Sectional Committee - Food and Agriculture Division Council. New Delhi,
India, 11pp. http://cgwb.gov.in/Documents/WQ-standards.pdf. Downloaded on 30
July 2020.
Blake, S., S.L. Deem, S. Strindberg, F. Maisels, L. Momont, I.-B.
Isia, I. Douglas-Hamilton, W.B. Karesh & M.D. Kock (2008). Roadless wilderness area
determines forest elephant movements in the Congo Basin. PloS One 3(10):
e3546. https://doi.org/https://doi.org/10.1371/journal.pone.0003546
Borda-de-Água L., R. Barrientos, P. Beja & H.M. Pereira
(Eds.) (2017). Railway Ecology. Springer Nature, Cham, xxx+318pp. https://doi.org/10.1007/978-3-319-57496-7
Borkar, M.R. (2018). First definitive record of a whip
scorpion Labochirus tauricornis (Pocock, 1900) from Goa, India: with
notes on its morphometry and pedipalp micro-morphology. Journal of
Threatened Taxa 10(7): 11955–11962. https://doi.org/10.11609/jott.4084.10.7.11955-11962
Borkar, M.R., N. Komarpant & D.B. Bastawade (2006). First report of Whip
Spider Phrynicus phipsoni Pocock from the human habitations and
protected areas of Goa state, India; with notes on its habits and habitat. Records
of the Zoological Survey of India: 106(Part 4): 33–38.
Braid, R.B., M. Schweitzer, S.A. Carnes & E.J. Soderstrom
(1985).
The importance of cumulative impacts for socioeconomic impact assessment and
mitigation. Energy 10(5): 643–652. https://doi.org/10.1016/0360-5442(85)90096-9
Burton, A.C., E. Neilson, D. Moreira, A. Ladle, R. Steenweg,
J.T. Fisher, E. Bayne & S. Boutin (2015). Wildlife camera trapping: a review
and recommendations for linking surveys to ecological processes. Journal of
Applied Ecology 52: 675–685. https://doi.org/10.1111/1365-2664.12432
Cain, A.T., V.R. Tuovila, D.G. Hewitt & M.E. Tewes
(2003).
Effects of a highway and mitigation projects on bobcats in Southern Texas. Biological
Conservation 114(2): 189–197. https://doi.org/10.1016/S0006-3207(03)00023-5
Case, R. (1978). Interstate highway road-killed animals: A data source
for biologists. Wildlife Society Bulletin 6(1): 8–13. https://doi.org/10.2307/3781058
Chen, X., X. Xia, Y. Zhao & P. Zhang (2010). Heavy metal
concentrations in roadside soils and correlation with urban traffic in Beijing,
China. Journal of Hazardous Materials 181(1–3): 640–646. https://doi.org/10.1016/j.jhazmat.2010.05.060
Chen, Z., R. Luo, Z. Huang, W. Tu, J. Chen, W. Li, S. Chen,
J. Xiao & Y. Ai (2015). Effects of different backfill soils on artificial soil
quality for cut slope revegetation: Soil structure, soil erosion, moisture
retention and soil C stock. Ecological Engineering 83: 5–12. https://doi.org/10.1016/j.ecoleng.2015.05.048
Chouvelon, T., E. Strady, M. Harmelin-Vivien, O. Radakovitch,
C. Brach-Papa, S. Crochet, J. Knoery, E. Rozuel, B. Thomas, J. Tronczynski
& J. Chiffoleau (2019). Patterns of trace metal bioaccumulation and trophic transfer
in a phytoplankton-zooplankton-small pelagic fish marine food web. Marine
Pollution Bulletin 146: 1013–1030. https://doi.org/10.1016/j.marpolbul.2019.07.047
Clausen, U., C. Doll, F.J. Franklin, G.V. Franklin, H.
Heinrichmeyer, J. Koshiek & W. Rothergatter (2012). Reducing railway noise
pollution. Policy department B: structural and cohesion policies, European
Parliament Committee on Transport and Tourism, Brussels, Belgium, 124pp. https://doi.org/10.1007/s13398-014-0173-7.2
Clevenger, A.P., B. Chruszcz & K.E. Gunson (2003). Spatial patterns and
factors influencing small vertebrate fauna road-kill aggregations. Biological
Conservation, 109(1): 15–26. https://doi.org/10.1016/S0006-3207(02)00127-1
Collins, S. (2004). Vocal fighting and flirting: the
functions of birdsong, pp. 39–79. In: Marler P. & H. Slabbekoorn (eds.). Nature’s
Music: The Science of Birdsong. Academic Press, 504pp. https://doi.org/10.1016/B978-012473070-0/50005-0
Comely, J.M.L. (2018). Iron ore mining and conflict in Goa:
An analysis of how mining is legitimised through EIAs, CSR and resistance. MS
thesis. Centre for Development and Environment, University of Oslo, xi+121pp.
Daniels, R.J.R. (2002). Freshwater Fishes of Peninsular
India. Universities Press, India, 288pp.
Das, A., H. Nagendra, M. Anand & M. Bunyan (2015). Topographic and
bioclimatic determinants of the occurrence of forest and grassland in tropical
montane forest-grassland mosaics of the Western Ghats, India. PloS One
10(6): e0130566. https://doi.org/https://doi.org/10.1371/journal.pone.0130566
Das, I. & K. Kunte (2005). New species of Nyctibatrachus
(Anura: Ranidae) from Castle Rock, Karnataka State, southwest India. Journal
of Herpetology 39(3): 465–470. https://doi.org/10.1670/198-04A.1
Datar, M. & P. Lakshminarasimhan (2011). Endemic plants of Bhagwan
Mahaveer National Park, Goa - an analysis based on their habitat, phenology and
life form types. The Indian Forester 137: 1451–1456.
Datar, M.N. & P. Lakshminarasimhan (2013). Check list of wild
angiosperms of Bhagwan Mahavir (Molem) National Park, Goa, India [with
erratum]. Check List 9(2): 186–207. https://doi.org/10.15560/9.2.186
Datar, M.N., S. Dongre & M. Gadgil (2019). A critical evaluation of
environmental impact assessments: a case study of Goa mines, India. Current
Science 117(5): 776–782. https://doi.org/10.18520/cs/v117/i5/776-782
Dinesh, K.P., C. Radhakrishnan, B.H. Channakeshavamurthy, P.
Deepak & N.U. Kulkarni (2020). A checklist of amphibians of India with IUCN
conservation status (Version 3.0). Zoological Survey of India, Kolkata. Downloaded
on 25 May 2020.
https://www.amphibians.org/wp-content/uploads/2020/05/2020_Indian_Amphibian_checklist.pdf
Douven, W. & J. Buurman (2013). Planning practice in
support of economically and environmentally sustainable roads in floodplains:
the case of the Mekong delta floodplains. Journal of Environmental
Management 128: 161–168. https://doi.org/10.1016/j.jenvman.2013.04.048
Dover, J. & J. Settele (2009). The influences of
landscape structure on butterfly distribution and movement: A review. Journal
of Insect Conservation 13: 3–27. https://doi.org/10.1007/s10841-008-9135-8
Duflo, E., M. Greenstone & N. Ryan (2013). Truth-telling by third-party
auditors and the response of polluting firms: experimental evidence from India.
The Quarterly Journal of Economics 128(4): 1499–1545. https://doi.org/10.1093/qje/qjt024
Dunkin, S.W., F.S. Guthery, S.J. Demaso, A.D. Peoples &
E.S. Parry (2009). Influence of anthropogenic structures on Northern Bobwhite
space use in western Oklahoma. The Journal of Wildlife Management 73(2):
253–259. https://doi.org/10.2193/2008-212
Dutta, T., S. Sharma & R. DeFries (2018). Targeting restoration
sites to improve connectivity in a tiger conservation landscape in India. PeerJ
10: e5587. https://doi.org/10.7717/peerj.5587
eBird (2017). eBird: An online database of bird distribution and
abundance. Cornell Lab of Ornithology, Ithaca, New York. Available:
http://www.ebird.org. Electronic version accessed 2 June 2020.
Eldegard, K., Ø. Totland & S.R. Moe (2015). Edge effects on plant
communities along power line clearings. Journal of Applied Ecology
52(4): 871–880. https://doi.org/10.1111/1365-2664.12460
Fahrig, L., J.H. Pedlar, S.E. Pope, P.D. Taylor & J.F.
Wegner (1995). Effect of road traffic on amphibian density. Biological Conservation
73(3): 177–182. https://doi.org/https://doi.org/10.1016/0006-3207(94)00102-V
Ferreira, M.P., M. Zortea, D.C. Zanotta, Y.E. Shimabukuro
& C.R. de Souza Filho (2016). Mapping tree species in tropical seasonal
semi-deciduous forests with hyperspectral and multispectral Data. Remote
Sensing of Environment 179 (June): 66–78. https://doi.org/10.1016/j.rse.2016.03.021
Ferrell, S.M. & P.T. Lautala (2010). Rail Embankment
Stabilization on Permafrost – Global Experiences. Michigan Tech Transportation
Institute, Michigan Technological University, 25pp.
Font, A., T. Baker, I.S. Mudway, E. Purdie, C. Dunster &
G.W. Fuller (2014). Degradation in urban air quality from construction activity
and increased traffic arising from a road widening scheme. Science of the
Total Environment 497–498: 123–132. https://doi.org/10.1016/j.scitotenv.2014.07.060
Francis, C.D., C.P. Ortega & A. Cruz (2009). Noise pollution changes
avian communities and species interactions. Current Biology 19:
1415–1419. https://doi.org/10.1016/j.cub.2009.06.052
Gad, S.D. & S.K. Shyama (2009). Studies on the food and
feeding habits of Gaur Bos gaurus H. Smith (Mammalia: Artiodactyla:
Bovidae) in two protected areas of Goa. Journal of Threatened Taxa 1(2):
128–130. https://doi.org/10.11609/JoTT.o1589.128-30
Garriga, N., X. Santos, A. Montori, A. Richter-Boix, M.
Franch & G.A. Llorente (2012). Are protected areas truly protected? The impact of
road traffic on vertebrate fauna. Biodiversity and Conservation 21:
2761–2774. https://doi.org/10.1007/s10531-012-0332-0
Gillan, J.K., E.K. Strand, J.W. Karl, K.P. Reese & T.
Laninga (2013). Using spatial statistics and point-pattern simulations to assess the
spatial dependency between greater sage-grouse and anthropogenic features. Wildlife
Society Bulletin 37(2): 301–310. https://doi.org/https://doi.org/10.1002/wsb.272
Goosem, M. (1997). Internal fragmentation: The effects
of roads, highways and powerline clearings on movements and mortality of
rainforest vertebrates, pp. 241–255. In: Laurance W.F. & R.O. Bierregaard
(eds.). Tropical Forest Remnants: Ecology, Management, and Conservation of
Fragmented Communities. University of Chicago Press, Chicago, Illinois,
632pp.
Goosem, M. (2002). Effects of tropical rainforest roads
on small mammals: Fragmentation, edge effects and traffic disturbance. Wildlife
Research 29(3): 277–289. https://doi.org/10.1071/WR01058
Goosem, M. (2007). Fragmentation impacts caused by
roads through rainforests. Current Science 93(11): 1587–1595.
Goosem, M., E.K. Harding, G. Chester, N. Tucker, C. Harriss
& K. Oakley (2010). Roads in Rainforest: Best Practice Guidelines for Planning,
Design and Management. Guidelines prepared for the Queensland Department of
Transport and Main Roads and the Australian Government’s Marine and Tropical
Sciences Research Facility. Reef and Rainforest Research Centre Limited,
Cairns, 64pp.
Goosem, M. & H. Marsh (1997). Fragmentation of a Small-mammal
Community by a Powerline Corridor through Tropical Rainforest. Wildlife
Research 24(5): 613–629. https://doi.org/10.1071/WR96063
Gosavi, N., A. Bayani, A. Khandekar, P. Roy & K. Kunte
(Eds.) (2020). Amphibians of India, v. 1.05. Indian Foundation for Butterflies.
Electronic
version accessed 08 July 2020. http://www.indianamphibians.org
Grubh, R.B. & S. Ali (1976). Birds of Goa. Journal of the
Bombay Natural History Society 73(1): 42–53.
Gubbi, S., K. Mukherjee, M. Swaminath & H. Poornesha
(2016).
Providing more protected space for tigers Panthera tigris: A landscape
conservation approach in the Western Ghats, southern India. Oryx 50(2):
336–343. https://doi.org/https://doi.org/10.1017/S0030605314000751
Gubbi, S., H.C. Poornesha & M.D. Madhusudan (2012). Impact of vehicular
traffic on the use of highway edges by large mammals in a south Indian wildlife
reserve. Current Science 102(7): 1047–1051.
Hamel, S., S.T. Killengreen, J. Henden, N.E. Eide, L.
Roed-eriksen, R.A. Ims & N.G. Yoccoz (2013). Towards good practice guidance in
using camera-traps in ecology: influence of sampling design on validity of
ecological inferences. Methods in Ecology and Evolution 4(2):
105–113. https://doi.org/10.1111/j.2041-210x.2012.00262.x
Hayward, M.W., L. Boitani, N.D. Burrows, P.J. Funston, K.U.
Karanth, D.I. Mackenzie, K.H. Pollock & R.W. Yarnell (2015). Ecologists need robust
survey designs, sampling and analytical methods. Journal of Applied Ecology
52: 286–290. https://doi.org/10.1111/1365-2664.12408
Holderegger, R. & M. Di Giulio (2010). The genetic effects of
roads: A review of empirical evidence. Basic and Applied Ecology 11:
522–531. https://doi.org/10.1016/j.baae.2010.06.006
Hoskin, C.J. & M.W. Goosem (2010). Road Impacts on
abundance, call traits, and body size of rainforest frogs in Northeast
Australia. Ecology and Society 15(3): 15. [online]. http://www.ecologyandsociety.org/vol15/iss3/art15/
Husejnovic, M. S., M. Bergant, S. Jankovic, S. Zizek, A.
Smajlovic, A. Softic, O. Music & B. Antonijevic (2018). Assessment of Pb, Cd and
Hg soil contamination and its potential to cause cytotoxic and genotoxic
effects in human cell lines (CaCo-2 and HaCaT). Environmental Geochemistry
and Health 40(4): 1557–1572. https://doi.org/10.1007/s10653-018-0071-6
IARC (1989). Diesel and Gasoline Engine Exhausts and Some
Nitroarenes. IARC Monographs on the Evaluation of Carcinogenic Risk to
Humans, Vol. 105. International Agency for Research on Cancer Lyon, France,
703pp.
Jaren, V., R. Andersen, M. Ulleberg, P. Pedersen & B.
Wiseth (1991). Moose-train collisions: The effects of vegetation removal with a cost-benefit
analysis. Alces 27(1): 93–99.
Jayadevan, A., R. Nayak, K.K. Karanth, J. Krishnaswamy, R.
DeFries, K.U. Karanth & S. Vaidyanathan (2020). Navigating paved paradise:
Evaluating landscape permeability to movement for large mammals in two
conservation priority landscapes in India. Biological Conservation 247:
108613. https://doi.org/10.1016/j.biocon.2020.108613
Jayamurugan, R., B. Kumaravel, S. Palanivelraja & M.P.
Chockalingam (2013). Influence of Temperature, Relative Humidity and Seasonal
Variability on Ambient Air Quality in a Coastal Urban Area. International
Journal of Atmospheric Sciences. Volume 2013. Article ID 264046. https://doi.org/10.1155/2013/264046
Jenkins, A.R., J.M. Shaw, J.J. Smallie, B. Gibbons, R.
Visagie & P.G. Ryan (2011). Estimating the impacts of power line collisions on
Ludwig’s Bustards Neotis ludwigii. Bird Conservation International
21(3): 303–310. https://doi.org/10.1017/S0959270911000128
Jhala, Y.V., Q. Qureshi & A.K. Nayak (Eds.) (2020). Status of tigers,
copredators and prey in India, 2018. National Tiger Conservation Authority,
Government of India, New Delhi, and Wildlife Institute of India, Dehradun,
650pp.
Johnson, A.J. & M. Arunachalam (2010). Habitat Use of fishes in
streams of Kalakad Mundanthurai Tiger Reserve, India. International Journal
of Ecology & Development 17(3): 1–14.
Joshi, A., S. Vaidyanathan, S. Mondol, A. Edgaonkar & U.
Ramakrishnan (2013). Connectivity of tiger (Panthera tigris) populations
in the human-influenced forest mosaic of central India. PloS One 8(11):
e77980. https://doi.org/https://doi.org/10.1371/journal.pone.0077980
Joshi, V.C. & M.K. Janarthanam (2004). The diversity of
life-form type, habitat preference and phenology of the endemics in the Goa
region of the Western Ghats, India. Journal of Biogeography 31(8):
1227–1237. https://doi.org/10.1111/j.1365-2699.2004.01067.x
Karanth, K.U., A.M. Gopalaswamy, N.S. Kumar, S. Vaidyanathan,
J.D. Nichols & D.I. MacKenzie (2011). Monitoring carnivore populations at
the landscape scale: occupancy modelling of tigers from sign surveys. Journal
of Applied Ecology 48(4): 1048–1056. https://doi.org/10.1111/j.1365-2664.2011.02002.x
Kerkar, R.P. (2020). 4th tiger found dead in 4
days in Sattari forest. Electronic version accessed on 09 January 2020. https://timesofindia.indiatimes.com/city/goa/4th-tiger-found-dead-in-4-days-in-sattari-forest/articleshow/73163428.cms
Kerley, L.L., J.M. Goodrich, D.G. Miquelle, E.N. Smirnov,
H.B. Quigley & M.G. Hornocker (2002). Effects of roads and human
disturbance on Amur Tigers. Conservation Biology 16: 97–108. https://doi.org/10.2307/3061403
Khera, N. & A. Kumar (2010). Inclusion of biodiversity in
environmental impact assessments (EIA): a case study of selected EIA reports in
India. Impact Assessment and Project Appraisal 28(3): 189–200. https://doi.org/10.3152/146155110X12772982841005
Kowarik, I. & M. von der. Lippe (2011). Secondary wind dispersal
enhances long-distance dispersal of an invasive species in urban road
corridors. NeoBiota 9: 49–70.
Krupa, H., A. Borker & A. Gopal (2017). Photographic record of
sympatry between Asian Small-Clawed Otter and Smooth-Coated Otter in the
northern Western Ghats, India. IUCN Otter Specialist Group Bulletin
34(1): 51–57.
Kulkarni, N., K.P. Dinesh, P. Prashanth, G. Bhatta & C.
Radhakrishnan (2013). Checklist of Amphibians of Goa. Frog leg 19: 7–12.
Kumar, A. & R.K. Somashekar (2008). Environmental Science
and Technology in India. Daya Publishing House, Delhi, 500pp.
Kumar, R. & K.R. Devi (2013). Conservation of freshwater habitats
and fishes in the Western Ghats of India. International Zoo Yearbook
47(1): 71–80. https://doi.org/10.1111/izy.12009
Lama, A.K. & H. Job (2014). Protected Areas and Road
development: Sustainable development discourses in the Annapurna Conservation
Area, Nepal. Erdkunde 68(4): 229–250. https://doi.org/10.3112/erdkunde.2014.04.01
Lampe, U., K. Reinhold & T. Schmoll (2014). How grasshoppers respond
to road noise: Developmental plasticity and population differentiation in
acoustic signalling. Functional Ecology 28(3): 660–668. https://doi.org/10.1111/1365-2435.12215
Lampila, P., M. Mönkkönen & A. Desrochers (2005). Demographic Responses by
Birds to Forest Fragmentation. Conservation Biology 19(5): 1537–1546. https://doi.org/10.1111/j.1523-1739.2005.00201.x
Larsen, M.C. & J.E. Parks (1998). How wide is a road? The
association of roads and mass-wasting in a forested montane environment. Earth
Surface Processes and Landforms 22(9): 835–848. https://doi.org/https://doi.org/10.1002/(SICI)1096-9837(199709)22:9<835::AID-ESP782>3.0.CO;2-C
Larsen, M.C. & A.J. Torres-Sánchez (1998). The frequency and
distribution of recent landslides in three montane tropical regions of Puerto
Rico. Geomorphology 24(4): 309–331. https://doi.org/10.1016/S0169-555X(98)00023-3
Laurance, W.F., M. Goosem & S.G.W. Laurance (2009). Impacts of roads and
linear clearings on tropical forests. Trends in Ecology & Evolution
24: 659–669. https://doi.org/10.1016/j.tree.2009.06.009
Laurance, W.F. (2015). Wildlife struggle in an increasingly
noisy world. Proceedings of the National Academy of Sciences 112(39):
11995–11996. https://doi.org/10.1073/pnas.1516050112
Levengood, J.M., E.J. Heske, P.M. Wilkins & J.W. Scott
(2015).
Polyaromatic hydrocarbons and elements in sediments associated with a suburban
railway. Environmental Monitoring and Assessment 187: 534 (2015). https://doi.org/10.1007/s10661-015-4757-2
Loss, S.R., T. Will & P.P. Marra (2014). Refining Estimates of
Bird Collision and Electrocution Mortality at Power Lines in the United States.
PloS One 9(7): e101565. https://doi.org/https://doi.org/10.1371/journal.pone.0101565
Lucas, P.S., R.G. de Carvalho & C. Grilo (2017). Railway Disturbances on
Wildlife: Types, Effects, and Mitigation Measures, pp. 81–99. In:
Borda-de-Água, L., R. Barrientos, P. Beja & H.M. Pereira (eds.). Railway
Ecology. Springer International Publishing, Cham, xxx+320pp. https://doi.org/10.1007/978-3-319-57496-7_6
Luce, C.H. & R. Mountain (2002). Hydrological processes
and pathways affected by forest roads: What do we still need to learn? Hydrological
Process, 16: 2901–2904. https://doi.org/10.1002/hyp.5061
Maelfait, J.-P. &
F. Hendrickx (1998). Spiders as bio-indicators of anthropogenic stress in natural
and semi-natural habitats in Flanders (Belgium): some recent developments, pp.
293–300. In: Selden, P.A. (ed.). Proceedings of the 17th European
Colloquium of Arachnology. BAS, Edinburgh.
Manju, A., K. Kalaiselvi, V. Dhananjayan, G.S. Banupriya
& M.H. Vidhya (2018). Spatio-seasonal variation in ambient air pollutants and
influence of meteorological factors in Coimbatore, southern India. Air
Quality, Atmosphere & Health 11: 1179–1189. https://doi.org/10.1007/s11869-018-0617-x
Marler, P. (2004). Bird calls: A cornucopia for
communication, pp. 132–177. In: Marler, P. & H. Slabbekoorn (eds.). Nature’s
Music: The Science of Birdsong. Academic Press, 504pp. https://doi.org/10.1016/B978-012473070-0/50008-6
Meek, P.D., G. Ballard, A. Claridge, R. Kays, K. Moseby, T.
O’Brien, A. O’Connell, J. Sanderson, D.E. Swann, M. Tobler & S. Townsend
(2014).
Recommended guiding principles for reporting on camera trapping research. Biodiversity
and Conservation 23(9): 2321–2343. https://doi.org/10.1007/s10531-014-0712-8
Menon, V. (2014). Indian Mammals. A Field Guide.
Hachette India, Gurgaon, 528pp.
Meunier, G. & C. Lavoie (2012). Roads as corridors for
invasive plant species: New evidence from Smooth Bedstraw (Galium mollugo).
Invasive Plant Science and Management 5: 92–100. https://doi.org/10.1614/IPSM-D-11-00049.1
Molur, S., K.G. Smith, B.A. Daniel & W.R.T. Darwall
(2011).
The Status and Distribution of Freshwater Biodiversity in the Western Ghats,
India. International Union for Conservation of Nature, Cambridge, UK and
Gland, Switzerland and Zoo Outreach Organisation. Coimbatore, India, 116pp.
Mortensen, D., E. Rauschert, A. Nord & B. Jones (2009). Forest roads facilitate
the spread of invasive plants. Invasive Plant Science and Management 2:
191–199. https://doi.org/10.1614/IPSM-08-125.1
Mundahl, N.D., A.G. Bilyeu & L. Maas (2013). Bald Eagle nesting
habitats in the Upper Mississippi River National Wildlife and Fish Refuge. Journal
of Fish and Wildlife Management 4(2): 362–376. https://doi.org/10.3996/012012-jfwm-009
Muñoz, P.T., F.P. Torres & A.G. Megías (2015). Effects of roads on
insects: a review. Biodiversity and Conservation 24: 659–682. https://doi.org/10.1007/s10531-014-0831-2
Nayak, R., K.K. Karanth, T. Dutta, R. Defries, K.U. Karanth
& S. Vaidyanathan (2020). Bits and pieces: Forest fragmentation by linear intrusions
in India. Land Use Policy: 104619. https://doi.org/10.1016/j.landusepol.2020.104619
O’Connell, A.F., J.D. Nichols & K.U. Karanth (Eds.).
(2011). Camera
Traps in Animal Ecology. Springer, Japan, 271pp. https://doi.org/10.1007/978-4-431-99495-4
Padhye, A.D., N. Modak & N. Dahanukar (2014). Indirana chiravasi,
a new species of leaping frog (Anura: Ranixalidae) from Western Ghats of India.
Journal of Threatened Taxa 6(10): 6293–6312. https://doi.org/http://dx.doi.org/10.11609/JoTT.o4068.6293-312
Paliwal, R. (2006). EIA practice in India and its
evaluation using SWOT analysis. Environmental Impact Assessment Review
26: 492–510.
Pereira, P., A. Gimeìnez-Morera, A. Novara, S. Keesstra, A.
Jordán, R.E. Masto, E. Brevik, C. Azorin-Molina & A. Cerdà (2015). The impact of road and
railway embankments on runoff and soil erosion in eastern Spain. Hydrology
& Earth System Sciences 12: 12947–12985. https://doi.org/10.5194/hessd-12-12947-2015
Phaipasith, S. & J.-C. Castella (2017). Expansion of road
networks in upland production areas: Impacts on landscapes and livelihoods in
Huaphan Province, Lao PDR. EFICAS Project, CIRAD and DALAM, Ministry of
Agriculture and Forestry, Lao PDR, 84pp.
Pollom, R. (2016). Microphis cuncalus. In: The
IUCN Red List of Threatened Species 2016: e.T166639A60595076. Downloaded on 22
August 2020. https://doi.org/10.2305/IUCN.UK.2016-3.RLTS.T166639A60595076.en
Poor, E.E., V.I.M. Jati, M.A. Imron & M.J. Kelly (2019). The road to
deforestation: Edge effects in an endemic ecosystem in Sumatra, Indonesia. PloS
One 14(7): e0217540. https://doi.org/10.7294/w4-j92h-ka06
Prasad, M. & R.K. Varshney (1995). A check-list to the
Odonata of India including data on larval studies. Oriental Insects
29(1): 385–428. https://doi.org/10.1080/00305316.1995.10433748
Punjabi, G.A., A.S. Borker, F. Mhetar, D. Joshi, R. Kulkarni,
S.K. Alave & M.K. Rao (2014). Recent records of Stripe-necked Mongoose Herpestes
vitticollis and Asian Small-clawed Otter Aonyx cinereus from the
north Western Ghats, India. Small Carnivore Conservation 51: 51–55.
Putman, R.J. (1997). Deer and road traffic accidents:
Options for management. Journal of Environmental Management 51(1):
43–57. https://doi.org/10.1006/jema.1997.0135
Qin, Z., X. Wei & Y. Qing (2014). Study on environmental
protection of highway construction on Birds Nature Reserve. Nature
Environment and Pollution 13(4): 831–834.
Radhakrishna, S. & M. Singh (2002). Conserving the Slender
Loris (Loris lydekkerianus lydekkerianus), pp. 227–231. In: Proceedings
of the National Seminar on Conservation of Eastern Ghats. Environment
Protection Training Research Institute, Hyderabad.
Rahmani, A.R., M.Z. Islam & R. Kasambe (eds.) (2016). Important Bird and
Biodiversity Areas in India - Priority Sites for Conservation (Revised and
updated), 2nd edition, Vol. I. Bombay Natural History Society,
Indian Bird Conservation Network, Royal Society for the Protection of Birds and
BirdLife International (U.K.), pp.i-xii+1992.
Rajaram, T. & A. Das (2011). Screening for EIA in India:
Enhancing effectiveness through ecological carrying capacity approach. Journal
of Environmental Management 92(1): 140–148. https://doi.org/10.1016/j.jenvman.2010.08.024
Raman, T.R.S. (2011). Framing ecologically sound policy on
linear intrusions affecting wildlife habitats. Background paper for the
National Board for Wildlife. Nature Conservation Foundation, Mysore, 43pp.
Rangnekar, P. & O. Dharwadkar (2009). Three additions to the
known butterfly (Lepidoptera: Rhopalocera and Grypocera) fauna of Goa, India. Journal
of Threatened Taxa 1(5): 298–299. https://doi.org/10.11609/jott.o2140.298-9
Rangnekar, P. & R. Naik (2014). Further additions to the
Odonata (Insecta) fauna of Goa, India. Journal of Threatened Taxa 6(3):
5585–5589. https://doi.org/10.11609/JoTT.o3641.5585-9
Rangnekar, P., M. Borkar & O. Dharwadkar (2010). Additions to the Odonata
(Insecta) of Goa. Journal of Threatened Taxa 2(4): 805–814. https://doi.org/10.11609/JoTT.o2286.805-14
Rangnekar, P., O. Dharwadkar, K. Sadasivan & K.A.
Subramanian (2019). New species of Cyclogomphus Selys, 1854 (Insecta:
Odonata: Gomphidae) from the Western Ghats, India with comments on the status
of Cyclogomphus vesiculosus Selys, 1873. Zootaxa 4656(3): 515–524.
Rasmussen, P.C. & J.C. Anderton (2012). Birds of South Asia -
The Ripley Guide, Vol.1. Lynx Edicions, Barcelona, 1067pp.
Ratner, B.D., D.B. Rahut, M. Käkönen, H. Navy, M. Keskinen,
S. Yim, L. Suong & R. Chuenpagdee (2007). Influence of built structures on
local livelihoods: case studies of road development, irrigation and fishing
lots. Report submitted to Kingdom of Cambodia, 50pp.
Ries, L. & D.M. Debinski (2001). Butterfly responses to
habitat edges in the highly fragmented prairies of Central Iowa. Journal of
Animal Ecology 70(5): 840–852. https://doi.org/10.1046/j.0021-8790.2001.00546.x
Rioux, S., J.-P. Savard & A.A. Gerick (2013). Avian mortalities due to
transmission line collisions: a review of current estimates and field methods
with an emphasis on applications to the Canadian electric network. Avian
Conservation and Ecology 8(2): 7. https://doi.org/http://dx.doi.org/10.5751/ACE-00614-080207
Roberts, P.T., S.B. Reid, D.S. Eisinger, D.L. Vaughn, E.K.
Pollard, J.L. DeWinter, Y. Du, A.E. Ray & S.G. Brown (2010). Construction activity,
emissions, and air quality impacts: real-world observations from an Arizona
road-widening case study. Sonoma Technology Inc., Arizona Department of
Transportation, 195pp.
Roy, P.S., M.D. Behera, M.S.R. Murthy, A. Roy, S. Singh,
S.P.S. Kushwaha, C.S. Jha, S. Sudhakar, P.K. Joshi, C.S. Reddy, S. Gupta &
R.M. Ramachandran (2015). New vegetation type map of India prepared using satellite
remote sensing: Comparison with global vegetation maps and utilities. International
Journal of Applied Earth Observation and Geoinformation 39: 142–159. https://doi.org/https://doi.org/10.1016/j.jag.2015.03.003
Santhoshkumar, S., P. Kannan, A. Veeramani, A. Samson, S.
Karthick & J. Leonaprincy (2017). A preliminary report on the impact
of road kills on the herpetofauna species in Nilgiris, Tamil Nadu, India. Journal
of Threatened Taxa 9(3): 10004–10010. https://doi.org/10.11609/jott.3001.9.3.10004-10010
Sengupta, A. & S. Radhakrishna (2013). Of concern yet?
Distribution and conservation status of the Bonnet Macaque (Macaca radiata)
in Goa, India. Primate Conservation 27: 109–114.
Seshadri, K. & T. Ganesh (2011). Faunal mortality on roads
due to religious tourism across time and space in protected areas: A case study
from south India. Forest Ecology and Management 262: 1713–1721. https://doi.org/10.1016/j.foreco.2011.07.017
Sharma, R.C. (1976). Records of the reptiles of Goa. Records
of the Zoological Survey of India 71: 149–167.
Sheth, C., M.F. Ahmed, S. Banerjee, N. Dahanukar, S. Dalvi,
A. Datta, A.D. Roy, K. Gogoi, M. Gogoi, S. Joshi, A. Kamdar, J. Krishnaswamy,
M. Kumar, R.K. Menzies, S. Molur, S. Mukherjee, R. Naniwadekar, S. Nijhawan, R.
Raghavan, M. Rao, J.K. Roy, N. Sharma, A. Sinha, U. Srinivasan, K. Tamma, C.
Umbrey, N. Velho, A Vishwanathan & R. Yumnam (2020). ‘The devil is in the
detail ‘: Peer-review of the Wildlife Conservation Plan by the Wildlife
Institute of India for the Etalin Hydropower Project, Dibang Valley. Zoo’s
Print 35(5): 1–78. https://zoosprint.zooreach.org/index.php/zp/article/view/5686/5103
Shubhalaxmi, V., R.C. Kendrick, A. Vaidya, N. Kalagi & A.
Bhagwat (2011). Inventory of moth fauna (Lepidoptera: Heterocera) of the northern
western Ghats, Maharashtra, India. Journal of the Bombay Natural History
Society 108(3): 183–205.
Sidle, R.C. & A.D. Ziegler (2012). The dilemma of mountain
roads. Nature Geoscience 5: 437–438.
Sidle, R.C., A.D. Ziegler, J.N. Negishi, A.R. Nik, R. Siew
& F. Turkelboom (2006). Erosion processes in steep terrain—Truths, myths, and
uncertainties related to forest management in Southeast Asia. Forest Ecology
and Management 224(1–2): 199–225. https://doi.org/10.1016/j.foreco.2005.12.019
Simaika, J.P., M.J. Samways & P.P. Frenzel (2016). Artificial ponds increase
local dragonfly diversity in a global biodiversity hotspot. Biodiversity and
Conservation 25: 1921–1935. https://doi.org/10.1007/s10531-016-1168-9
Slabbekoorn, H. & W. Halfwerk (2009). Behavioural ecology:
noise annoys at community level. Current Biology 19: 693–695. https://doi.org/10.1016/j.cub.2009.07.002
Sollmann, R., A. Mohamed, H. Samejima & A. Wilting
(2013).
Risky business or simple solution – Relative abundance indices from
camera-trapping. Biological Conservation 159: 405–412. https://doi.org/10.1016/j.biocon.2012.12.025
Sreekantha, M.D. Subash Chandran, D.K. Mesta, G.R. Rao, K.V.
Gururaja & T.V. Ramachandra (2007). Fish diversity in relation to
landscape and vegetation in central Western Ghats, India. Current Science 92(11):
1592–1603.
Subramanian, K.A., P. Rangnekar & R. Naik (2013). Idionyx (Odonata:
Corduliidae) of the Western Ghats with a description of a new species. Zootaxa
3652(2): 277–288. https://doi.org/10.11646/zootaxa.3652.2.5
Świetlik, R., M. Strzelecka & M. Trojanowska (2013). Evaluation of
traffic-related heavy metals emissions using noise barrier road dust analysis. Polish
Journal of Environmental Studies 22(2): 561–567.
Talwar, P.K. & A.G. Jhingran (Eds.) (1991). Inland fishes of India
and adjacent countries, Vol 1 & 2. Oxford & IBH Publishing
Company, pp. xxxiv+1158.
Thatte, P., A. Joshi, S.
Vaidyanathan, E. Landguth & U. Ramakrishnan (2018). Maintaining
tiger connectivity and minimizing extinction into the next century: Insights
from landscape genetics and spatially-explicit simulations. Biological
Conservation 218: 181–191. https://doi.org/https://doi.org/10.1016/j.biocon.2017.12.022
The Goan Everyday (2019). Camera
trap captures tiger’s presence in Mollem. Electronic version accessed 27
December 2020. https://www.thegoan.net//camera-trap-captures-tiger%E2%80%99s-presence-in-mollem/51600.html
Trombulak, S.C. & C.A. Frissell
(2000). Review of Ecological Effects of Roads on Terrestrial
and Aquatic Communities. Conservation Biology 14(1): 18–30. https://doi.org/https://doi.org/10.1046/j.1523-1739.2000.99084.x
Uddin, M. 2017.
Assessing threats to birds from power-lines in Thar with special emphasis on
Great Indian Bustard. MSc Thesis. Department of Wildlife Science, University of
Kota, Rajasthan.
Walelign, S.Z., M.R. Nielsen &
J.B. Jacobsen (2019). Roads and livelihood activity
choices in the Greater Serengeti Ecosystem, Tanzania. PloS One 14(3):
e0213089. https://doi.org/https://doi.org/10.1371/journal.pone.0213089
Wendling, Z.A., J.W. Emerson, A. de
Sherbinin, D.C. Esty et al. (2020). 2020
Environmental Performance Index. Yale Center for Environmental Law &
Policy, New Haven, CT. Electronic version accessed 25 July 2020. https://epi.yale.edu/
Wikipedia contributors (2020).
Flora and fauna of Goa. In: Wikipedia, The Free Encyclopedia, 4 May 2020.
Downloaded on 23 June 2020.
Wiłkomirski, B., B.
Sudnik-Wójcikowska, H. Galera, M. Wierzbicka & M. Malawska (2011).
Railway transportation as a serious source of organic and inorganic pollution. Water,
Air, & Soil Pollution 218: 333–345. https://doi.org/10.1007/s11270-010-0645-0
Wiłkomirski, B., H. Galera, B.
Sudnik-Wójcikowska, T. Staszewski & M. Malawska (2012).
Railway Tracks - Habitat Conditions, Contamination, Floristic Settlement - A
Review. Environment and Natural Resources Research 2(1): 86–95. https://doi.org/10.5539/enrr.v2n1p86
WII (2016).
Eco-friendly measures to mitigate the impacts of linear infrastructure on
wildlife. Wildlife Institute of India, Dehradun, India, 151pp.
Xue, X., H. Hong & A.T. Charles
(2004). Cumulative environmental impacts and integrated
coastal management: The case of Xiamen, China. Journal of Environmental
Management 71(3): 271–283. https://doi:10.1016/j.jenvman.2004.03.006.
Zhang, X., H. Yang & Z. Cui (2018). Evaluation and analysis of soil migration and distribution
characteristics of heavy metals in iron tailings. Journal of Cleaner
Production 172: 475–480. https://doi.org/10.1016/j.jclepro.2017.09.277
Appendix
I. Checklist of birds in Bhagwan Mahavir Sanctuary and National Park.
The
List is compiled from data available on eBird (2017) from multiple hotspots and
checklist locations within BMWS NP and Rahmani et al. (2016).
ENDEMISM
TO WG (WESTERN GHATS): Species, whose global distribution range is restricted
to within the biogeographical boundaries of the Western Ghats. In other words,
they are unique to Western Ghats, and are not found anywhere else in the world.
IUCN:
Evaluation of species as per IUCN Redlist 2020-1 CR: Critically Endangered; EN:
Endangered; VU: Vulnerable; NT: Near Threatened
WPA
(1972): Species listed and protected under five different categories (Schedule
I to IV, and VI) in accordance to the Wildlife Protection Act of 1972
STATUS:
Evaluation of migratory status of a species. R: Resident; M: Migrant; LM: Local
Migrant, making short movements out of the political boundaries of Goa; R/M:
Resident population supplemented by a migratory population; VG: Vagrant
migrants recorded away from their known migratory range; S: Residents of the
Indian Subcontinent with no known resident populations in Goa attributed to as
stray; UC: Unclear
RARITY: A species that has less
than ten independently confirmed records form within the political boundaries
of Goa, post 2000.
|
|
Species |
Endemism
to WG |
IUCN |
WLPA
(1972) |
Status |
Rarity |
|
|
I.
Anseriformes |
|
|
|
|
|
|
|
1. Anatidae (Ducks, geese,
swans) |
|
|
|
|
|
|
1 |
Lesser Whistling Duck Dendrocygna
javanica |
|
|
4 |
R |
|
|
|
II.Galliformes |
|
|
|
|
|
|
|
2. Phasianidae (partridges,
pheasants, grouse) |
|
|
|
|
|
|
2 |
Indian Peafowl Pavo cristatus |
|
|
1 |
R |
|
|
3 |
Jungle Bush Quail Perdicula
asiatica |
|
|
4 |
R |
|
|
4 |
Grey Junglefowl Gallus
sonneratii |
|
|
2 |
R |
|
|
5 |
Red Spurfowl Galloperdix
spadicea |
|
|
4 |
R |
|
|
|
III.
Columbiformes |
|
|
|
|
|
|
|
3. Columbidae (pigeons) |
|
|
|
|
|
|
6 |
Rock Pigeon Columba livia |
|
|
4 |
R |
|
|
7 |
Nilgiri Wood Pigeon Columba
elphinstonii |
|
VU |
4 |
R |
|
|
8 |
Oriental Turtle Dove Streptopelia
orientalis |
|
|
4 |
R |
|
|
9 |
(Western) Spotted Dove Streptopelia
chinensis suratensis |
|
|
4 |
R |
|
|
10 |
Orange-breasted Green Pigeon Treron
bicinctus |
|
|
4 |
R |
|
|
11 |
Grey-fronted Green Pigeon Treron
affinis |
|
|
4 |
R |
|
|
12 |
Asian Emerald Dove Chalcophaps
indica |
|
|
4 |
R |
|
|
13 |
Green Imperial Pigeon Ducula
aenea |
|
|
4 |
R |
|
|
14 |
Mountain Imperial Pigeon
(Nilgiri Imperial Pigeon) Ducula badia cuprea |
|
|
4 |
R |
|
|
|
IV.
Caprimulgiformes |
|
|
|
|
|
|
|
4. Podargidae (frogmouths) |
|
|
|
|
|
|
15 |
Sri Lanka Frogmouth Batrachostomus
moniliger |
|
|
1 |
R |
|
|
|
5. Caprimulgidae (nightjars) |
|
|
|
|
|
|
16 |
Jungle Nightjar Caprimulgus
indicus |
|
|
4 |
R |
|
|
17 |
Jerdon's Nightjar Caprimulgus
atripennis |
|
|
4 |
R |
|
|
18 |
Indian Nightjar Caprimulgus
asiaticus |
|
|
4 |
R |
X |
|
19 |
Savanna Nightjar Caprimulgus
affinis |
|
|
4 |
R |
|
|
|
6. Hemiprocnidae (Treeswifts) |
|
|
|
|
|
|
20 |
Crested Treeswift Hemiprocne
coronata |
|
|
|
R |
|
|
|
7. Apodidae (swifts) |
|
|
|
|
|
|
21 |
White-rumped Spinetail Zoonavena
sylvatica |
|
|
|
R |
|
|
22 |
Brown-backed Needletail Hirundapus
giganteus |
|
|
|
R |
|
|
23 |
Indian Swiftlet Aerodramus
unicolor |
|
|
1 |
R |
|
|
24 |
Asian Palm Swift Cypsiurus
balasiensis |
|
|
|
LM |
|
|
25 |
Alpine Swift Tachymarptis
melba |
|
|
|
R |
|
|
26 |
Indian House Swift Apus
affinis |
|
|
|
R |
|
|
27 |
Common Swift Apus apus |
|
|
|
M |
X |
|
|
V.
Cuculiformes |
|
|
|
|
|
|
|
8. Cuculidae (cuckoos) |
|
|
|
|
|
|
28 |
Greater Coucal Centropus
sinensis |
|
|
4 |
R |
|
|
29 |
Blue-faced Malkoha Phaenicophaeus
viridirostris |
|
|
4 |
R |
|
|
30 |
Pied Cuckoo Clamator
jacobinus |
|
|
4 |
R/M |
|
|
31 |
Asian Koel Eudynamys
scolopaceus |
|
|
4 |
R |
|
|
32 |
Banded Bay Cuckoo Cacomantis
sonneratii |
|
|
4 |
R |
|
|
33 |
Grey-bellied Cuckoo Cacomantis
passerinus |
|
|
4 |
R |
|
|
34 |
Fork-tailed Drongo Cuckoo Surniculus
dicruroides |
|
|
4 |
R |
|
|
35 |
Large Hawk Cuckoo Hierococcyx
sparverioides |
|
|
4 |
M |
X |
|
36 |
Common Hawk Cuckoo Hierococcyx
varius |
|
|
4 |
R |
|
|
37 |
Indian Cuckoo Cuculus
micropterus |
|
|
4 |
M |
X |
|
38 |
Common Cuckoo Cuculus canorus |
|
|
4 |
M |
|
|
|
VI.
Gruiformes |
|
|
|
|
|
|
|
9. Rallidae (rails and coots) |
|
|
|
|
|
|
39 |
Slaty-legged Crake Rallina
eurizonoides |
|
|
4 |
M |
|
|
40 |
White-breasted Waterhen Amaurornis
phoenicurus |
|
|
4 |
R |
|
|
41 |
Purple Swamphen Porphyrio
porphyrio |
|
|
4 |
R |
|
|
|
VII.
Ciconiiformes |
|
|
|
|
|
|
|
10. Ciconiidae (storks) |
|
|
|
|
|
|
42 |
Lesser Adjutant Leptoptilos
javanicus |
|
VU |
4 |
R |
|
|
43 |
Asian Openbill Anastomus
oscitans |
|
|
4 |
R |
|
|
44 |
Black Stork Ciconia nigra |
|
|
4 |
M |
X |
|
45 |
Woolly-necked Stork Ciconia
episcopus |
|
VU |
4 |
R |
|
|
|
11. Ardeidae (herons) |
|
|
|
|
|
|
46 |
Malayan Night Heron Gorsachius
melanolophus |
|
|
4 |
R |
|
|
47 |
Striated Heron Butorides
striata |
|
|
4 |
R |
|
|
48 |
Indian Pond Heron Ardeola
grayii |
|
|
4 |
R |
|
|
49 |
(Eastern) Cattle Egret Bubulcus
ibis coromandus |
|
|
4 |
R |
|
|
50 |
Grey Heron Ardea cinerea |
|
|
4 |
R/M |
|
|
51 |
Purple Heron Ardea purpurea |
|
|
4 |
R |
|
|
52 |
(Eastern) Great Egret Ardea
alba modesta |
|
|
4 |
R |
|
|
53 |
Intermediate Egret Ardea
intermedia |
|
|
4 |
R |
|
|
54 |
Little Egret Egretta garzetta |
|
|
4 |
R |
|
|
55 |
Western Reef Egret Egretta
gularis |
|
|
4 |
R |
|
|
|
12. Threskiornithidae (ibises) |
|
|
|
|
|
|
56 |
Black-headed Ibis Threskiornis
melanocephalus |
|
NT |
4 |
R/M |
|
|
|
VIII.
Suliformes |
|
|
|
|
|
|
|
13. Phalacrocoracidae
(cormorants) |
|
|
|
|
|
|
57 |
Little Cormorant Microcarbo
niger |
|
|
4 |
R |
|
|
58 |
Indian Cormorant Phalacrocorax
fuscicollis |
|
|
4 |
R |
|
|
|
14. Anhingidae (darters) |
|
|
|
|
|
|
59 |
Oriental Darter Anhinga
melanogaster |
|
NT |
4 |
R |
|
|
|
IX.
Charadriiformes |
|
|
|
|
|
|
|
15. Recurvirostridae (stilts and
avocets) |
|
|
|
|
|
|
60 |
Black-winged Stilt Himantopus
himantopus |
|
|
4 |
M |
|
|
|
16. Charadriidae (plovers &
lapwings) |
|
|
|
|
|
|
61 |
Little Ringed Plover Charadrius
dubius |
|
|
4 |
R |
|
|
62 |
Yellow-wattled Lapwing Vanellus
malabaricus |
|
|
4 |
R |
|
|
63 |
Red-wattled Lapwing Vanellus
indicus |
|
|
4 |
R |
|
|
|
17. Jacanidae (jacanas) |
|
|
|
|
|
|
64 |
Bronze-winged Jacana Metopidius
indicus |
|
|
4 |
R |
|
|
|
18. Scolopacidae (sandpipers) |
|
|
|
|
|
|
65 |
Common Snipe Gallinago
gallinago |
|
|
4 |
M |
|
|
66 |
Common Sandpiper Actitis
hypoleucos |
|
|
4 |
LM |
|
|
67 |
Green Sandpiper Tringa
ochropus |
|
|
4 |
M |
|
|
|
19. Turnicidae (buttonquails) |
|
|
|
|
|
|
68 |
Barred Buttonquail Turnix
suscitator |
|
|
4 |
R |
|
|
|
20. Glareolidae (coursers and
pratincoles) |
|
|
|
|
|
|
69 |
Little Pratincole Glareola
lactea |
|
|
|
M |
|
|
|
21. Laridae (gulls and terns) |
|
|
|
|
|
|
70 |
Gull-billed Tern Gelochelidon
nilotica |
|
|
4 |
R |
|
|
71 |
River Tern Sterna aurantia |
|
NT |
4 |
R |
|
|
|
X.
Accipitriformes |
|
|
|
|
|
|
|
22. Accipitridae (kites, hawks
and eagles) |
|
|
|
|
|
|
72 |
Black-winged Kite Elanus
caeruleus |
|
|
1 |
M |
|
|
73 |
Oriental Honey Buzzard Pernis
ptilorhynchus |
|
|
1 |
R |
|
|
74 |
Egyptian Vulture Neophron
percnopterus § |
|
EN |
1 |
S |
X |
|
75 |
Crested Serpent Eagle Spilornis
cheela |
|
|
1 |
R |
|
|
76 |
Short-toed Snake Eagle Circaetus
gallicus |
|
|
1 |
S |
|
|
77 |
White-rumped Vulture Gyps
bengalensis |
|
CR |
1 |
S |
X |
|
78 |
Indian Vulture Gyps indicus |
|
CR |
1 |
S |
X |
|
79 |
Mountain Hawk Eagle (Legge's
Hawk Eagle) Nisaetus nipalensis kelaarti |
|
|
1 |
R |
X |
|
80 |
Changeable Hawk Eagle (Crested
Hawk Eagle) Nisaetus cirrhatus cirrhatus |
|
|
1 |
R |
|
|
81 |
Rufous-bellied Eagle Lophotriorchis
kienerii |
|
|
1 |
R |
|
|
82 |
Black Eagle Ictinaetus
malaiensis |
|
|
1 |
R |
|
|
83 |
Bonelli's Eagle Aquila
fasciata |
|
|
1 |
R |
|
|
84 |
Booted Eagle Hieraaetus
pennatus |
|
|
1 |
M |
|
|
85 |
Western Marsh Harrier Circus
aeruginosus |
|
|
1 |
M |
|
|
86 |
Crested Goshawk Accipiter
trivirgatus |
|
|
1 |
R |
|
|
87 |
Shikra Accipiter badius |
|
|
1 |
R |
|
|
88 |
Besra Accipiter virgatus |
|
|
1 |
R |
|
|
89 |
Eurasian Sparrowhawk Accipiter
nisus |
|
|
1 |
M |
|
|
90 |
White-bellied Sea Eagle Haliaeetus
leucogaster |
|
|
1 |
R |
|
|
91 |
Grey-headed Fish Eagle Icthyophaga
ichthyaetus |
|
NT |
1 |
M |
X |
|
92 |
Brahminy Kite Haliastur indus |
|
|
1 |
R |
|
|
93 |
Black Kite Milvus migrans |
|
|
1 |
R/M |
|
|
94 |
White-eyed Buzzard Butastur
teesa |
|
|
1 |
R |
|
|
|
XI.
Strigiformes |
|
|
|
|
|
|
|
22. Tytonidae (barn owls) |
|
|
|
|
|
|
95 |
Sri Lanka Bay Owl Phodilus
assimilis |
|
|
4 |
R |
X |
|
96 |
Common Barn Owl Tyto alba |
|
|
4 |
R |
|
|
|
23. Strigidae (owls) |
|
|
|
|
|
|
97 |
Brown Hawk Owl Ninox scutulata |
|
|
4 |
R |
|
|
98 |
Jungle Owlet Glaucidium
radiatum |
|
|
4 |
R |
|
|
99 |
Spotted Owlet Athene brama |
|
|
4 |
R |
|
|
100 |
Oriental Scops Owl Otus sunia |
|
|
4 |
R |
|
|
101 |
Indian Scops Owl Otus
bakkamoena |
|
|
4 |
R |
|
|
102 |
Brown Wood Owl Strix
leptogrammica |
|
|
4 |
R |
|
|
103 |
Spot-bellied Eagle Owl Bubo
nipalensis |
|
|
4 |
R |
|
|
104 |
Brown Fish Owl Ketupa
zeylonensis |
|
|
4 |
R |
|
|
|
XII.
Trogoniformes |
|
|
|
|
|
|
|
24. Trogonidae (trogons) |
|
|
|
|
|
|
105 |
Malabar Trogon Harpactes
fasciatus |
|
|
4 |
R |
|
|
|
XIII.
Bucerotiformes |
|
|
|
|
|
|
|
25. Bucerotidae (hornbills) |
|
|
|
|
|
|
106 |
Great Hornbill Buceros
bicornis |
|
NT |
1 |
R |
|
|
107 |
Malabar Pied Hornbill Anthracoceros
coronatus |
|
NT |
1 |
R |
|
|
108 |
Malabar Grey Hornbill Ocyceros
griseus |
WG |
|
1 |
R |
|
|
109 |
Indian Grey Hornbill Ocyceros
birostris |
|
|
1 |
R |
|
|
|
26. Upupidae (hoopoes) |
|
|
|
|
|
|
110 |
Common Hoopoe Upupa epops |
|
|
|
R |
|
|
|
XIV.
Piciformes |
|
|
|
|
|
|
|
27. Picidae (woodpeckers) |
|
|
|
|
|
|
111 |
Speckled Piculet Picumnus
innominatus |
|
|
4 |
R |
|
|
112 |
Heart-spotted Woodpecker Hemicircus
canente |
|
|
4 |
R |
|
|
113 |
Common Golden-backed Woodpecker Dinopium
javanense |
|
|
4 |
R |
|
|
114 |
Lesser Golden-backed Woodpecker Dinopium
benghalense |
|
|
4 |
R |
|
|
115 |
Rufous Woodpecker Micropternus
brachyurus |
|
|
4 |
R |
|
|
116 |
Lesser Yellow-naped Woodpecker Picus
chlorolophus |
|
|
4 |
R |
|
|
117 |
White-bellied Woodpecker Dryocopus
javensis |
|
|
4 |
R |
|
|
118 |
Greater Golden-backed Woodpecker
Chrysocolaptes guttacristatus |
|
|
4 |
R |
|
|
119 |
White-naped Woodpecker Chrysocolaptes
festivus |
|
|
4 |
R |
|
|
120 |
Brown-capped Pygmy Woodpecker Dendrocopos nanus |
|
|
4 |
R |
|
|
121 |
Yellow-fronted Pied Woodpecker Dendrocopos
mahrattensis |
|
|
4 |
R |
|
|
|
28. Megalaimidae (barbets) |
|
|
|
|
|
|
122 |
Brown-headed Barbet Psilopogon
zeylanicus |
|
|
4 |
R |
|
|
123 |
White-cheeked Barbet Psilopogon
viridis |
|
|
4 |
R |
|
|
124 |
Malabar Barbet Psilopogon
malabaricus |
WG |
|
4 |
R |
|
|
125 |
Coppersmith Barbet Psilopogon
haemacephalus |
|
|
4 |
R |
|
|
|
XV.
Coraciiformes |
|
|
|
|
|
|
|
29. Meropidae (bee-eaters) |
|
|
|
|
|
|
126 |
Blue-bearded Bee-eater Nyctyornis
athertoni |
|
|
|
R |
|
|
127 |
Green Bee-eater Merops
orientalis |
|
|
|
R |
|
|
128 |
Chestnut-headed Bee-eater Merops
leschenaulti |
|
|
|
R |
|
|
129 |
Blue-tailed Bee-eater Merops
philippinus |
|
|
|
M |
|
|
130 |
Indian Roller Coracias
benghalensis |
|
|
4 |
LM |
|
|
131 |
European Roller Coracias
garrulus |
|
|
4 |
M |
|
|
|
30. Alcedinidae (kingfisher) |
|
|
|
|
|
|
132 |
Oriental Dwarf Kingfisher Ceyx
erithaca |
|
|
4 |
R |
|
|
133 |
Blue-eared Kingfisher Alcedo
meninting |
|
|
4 |
R |
|
|
134 |
Common Kingfisher Alcedo
atthis |
|
|
4 |
R |
|
|
135 |
Pied Kingfisher Ceryle rudis |
|
|
4 |
R |
|
|
136 |
Stork-billed Kingfisher Pelargopsis
capensis |
|
|
4 |
R |
|
|
137 |
White-throated Kingfisher Halcyon
smyrnensis |
|
|
4 |
R |
|
|
138 |
Black-capped Kingfisher Halcyon
pileata |
|
|
4 |
R |
|
|
|
XVI.
Falconiformes |
|
|
|
|
|
|
|
31. Falconidae (falcons and
caracaras) |
|
|
|
|
|
|
139 |
Common Kestrel Falco
tinnunculus |
|
|
4 |
M |
|
|
140 |
Amur Falcon Falco amurensis |
|
|
4 |
M |
|
|
141 |
Eurasian Hobby Falco subbuteo |
|
|
4 |
M |
|
|
142 |
Peregrine Falcon Falco
peregrinus |
|
|
1 |
|
|
|
|
XVII.
Psittaciformes |
|
|
|
|
|
|
|
32. Psittaculidae (Old World
parrots) |
|
|
|
|
|
|
143 |
Plum-headed Parakeet Psittacula
cyanocephala |
|
|
4 |
R |
|
|
144 |
Malabar Parakeet Psittacula
columboides |
WG |
|
4 |
R |
|
|
145 |
Rose-ringed Parakeet Psittacula
krameri |
|
|
4 |
R |
|
|
146 |
Vernal Hanging Parrot Loriculus
vernalis |
|
|
4 |
R |
|
|
|
XVIII.
Passeriformes |
|
|
|
|
|
|
|
33. Pittidae (pittas) |
|
|
|
|
|
|
147 |
Indian Pitta Pitta brachyura |
|
|
4 |
R |
|
|
|
34. Campephagidae (minivets and
cuckooshrikes) |
|
|
|
|
|
|
148 |
Small Minivet Pericrocotus
cinnamomeus |
|
|
4 |
R |
|
|
149 |
Scarlet Minivet (Orange Minivet)
Pericrocotus flammeus |
|
|
4 |
R |
|
|
150 |
Large (Indian) Cuckooshrike Coracina
javensis macei |
|
|
4 |
R |
|
|
151 |
Black-winged Cuckooshrike Lalage
melaschistos |
|
|
4 |
M |
X |
|
152 |
Black-headed Cuckooshrike Lalage
melanoptera |
|
|
4 |
R |
|
|
|
35. Oriolidae (orioles, figbirds
and allies) |
|
|
|
|
|
|
153 |
Black-hooded Oriole Oriolus
xanthornus |
|
|
4 |
R |
|
|
154 |
Indian Golden Oriole Oriolus
kundoo |
|
|
4 |
LM |
|
|
155 |
Black-naped Oriole Oriolus
chinensis |
|
|
4 |
M |
|
|
|
36. Artamidae (woodswallows,
Australian magpies and allies) |
|
|
|
|
|
|
156 |
Ashy Woodswallow Artamus
fuscus |
|
|
|
R |
|
|
|
37. Vangidae (vangas and
helmet-shrikes) |
|
|
|
|
|
|
157 |
Bar-winged Flycatcher-shrike Hemipus
picatus |
|
|
4 |
R |
|
|
158 |
Malabar Woodshrike Tephrodornis
sylvicola |
WG |
|
4 |
R |
|
|
159 |
Common Woodshrike Tephrodornis
pondicerianus |
|
|
4 |
R |
|
|
|
38. Aegithinidae (ioras) |
|
|
|
|
|
|
160 |
Common Iora Aegithina tiphia |
|
|
4 |
R |
|
|
|
39. Dicruridae (drongos) |
|
|
|
|
|
|
161 |
Black Drongo Dicrurus
macrocercus |
|
|
4 |
R |
|
|
162 |
Ashy Drongo Dicrurus
leucophaeus |
|
|
4 |
M |
|
|
163 |
White-bellied Drongo Dicrurus
caerulescens |
|
|
4 |
R |
|
|
164 |
Bronzed Drongo Dicrurus
aeneus |
|
|
4 |
R |
|
|
165 |
Hair-crested Drongo Dicrurus
hottentottus |
|
|
4 |
R |
|
|
166 |
Greater Racket-tailed Drongo Dicrurus
paradiseus |
|
|
4 |
R |
|
|
|
40. Rhipiduridae (fantails) |
|
|
|
|
|
|
167 |
White-spotted Fantail Rhipidura
albogularis |
|
|
4 |
R |
|
|
|
41. Laniidae (shrikes) |
|
|
|
|
|
|
168 |
Brown Shrike Lanius cristatus
cristatus |
|
|
|
M |
|
|
169 |
Isabelline Shrike Lanius
isabellinus |
|
|
|
M |
|
|
170 |
Long-tailed Shrike Lanius
schach |
|
|
|
M |
|
|
|
42. Corvidae (crows and jays) |
|
|
|
|
|
|
171 |
Rufous Treepie Dendrocitta
vagabunda |
|
|
4 |
R |
|
|
172 |
House Crow Corvus splendens |
|
|
5 |
R |
|
|
173 |
Large-billed Crow (Indian Jungle
Crow) Corvus macrorhynchos culminatus |
|
|
4 |
R |
|
|
|
43. Monarchidae (monarchs and
paradise-flycatchers) |
|
|
|
|
|
|
174 |
Black-naped Monarch Hypothymis
azurea |
|
|
4 |
R |
|
|
175 |
Indian Paradise-flycatcher Terpsiphone
paradisi |
|
|
4 |
LM |
|
|
|
44. Dicaeidae (flowerpeckers) |
|
|
|
|
|
|
176 |
Thick-billed Flowerpecker Dicaeum
agile |
|
|
4 |
R |
|
|
177 |
Pale-billed Flowerpecker Dicaeum
erythrorhynchos |
|
|
4 |
R |
|
|
178 |
Nilgiri Flowerpecker Dicaeum
concolor |
WG |
|
4 |
R |
|
|
|
45. Nectariniidae (sunbirds) |
|
|
|
|
|
|
179 |
Little Spiderhunter Arachnothera
longirostra |
|
|
4 |
R |
|
|
180 |
Purple-rumped Sunbird Leptocoma
zeylonica |
|
|
4 |
R |
|
|
181 |
Crimson-backed Sunbird Leptocoma
minima |
WG |
|
4 |
R |
|
|
182 |
Purple Sunbird Cinnyris
asiaticus |
|
|
4 |
R |
|
|
183 |
Loten's Sunbird Cinnyris
lotenius |
|
|
4 |
R |
|
|
184 |
Vigors's Sunbird Aethopyga
vigorsii |
WG |
|
4 |
R |
|
|
|
46. Irenidae (fairy-bluebirds) |
|
|
|
|
|
|
185 |
Asian Fairy-bluebird Irena
puella |
|
|
4 |
R |
|
|
|
47. Chloropseidae (leafbirds) |
|
|
|
|
|
|
186 |
Golden-fronted Leafbird Chloropsis
aurifrons |
|
|
4 |
R |
|
|
187 |
Jerdon's Leafbird Chloropsis
jerdoni |
|
|
4 |
R |
|
|
|
48. Ploceidae (weavers) |
|
|
|
|
|
|
188 |
Baya Weaver Ploceus
philippinus |
|
|
4 |
R |
|
|
|
49. Estrildidae (waxbills) |
|
|
|
|
|
|
189 |
Red Munia Amandava amandava |
|
|
4 |
R |
|
|
190 |
White-rumped Munia Lonchura
striata |
|
|
4 |
R |
|
|
191 |
Scaly-breasted Munia Lonchura
punctulata |
|
|
4 |
R |
|
|
192 |
Black-throated Munia Lonchura
kelaarti |
|
|
4 |
R |
|
|
193 |
Tricoloured Munia Lonchura
malacca |
|
|
4 |
R |
|
|
|
50. Passeridae (sparrows,
snowfinches and allies) |
|
|
|
|
|
|
194 |
House Sparrow Passer
domesticus |
|
|
4 |
R |
|
|
195 |
Yellow-throated Sparrow Gymnoris
xanthocollis |
|
|
4 |
R |
|
|
|
51. Motacillidae (wagtails and
pipits) |
|
|
|
|
|
|
196 |
Forest Wagtail Dendronanthus
indicus |
|
|
4 |
M |
|
|
197 |
Tree Pipit Anthus trivialis |
|
|
4 |
M |
|
|
198 |
Olive-backed Pipit Anthus
hodgsoni |
|
|
4 |
M |
X |
|
199 |
Paddyfield Pipit Anthus
rufulus |
|
|
4 |
R/M |
|
|
200 |
Tawny Pipit Anthus campestris |
|
|
4 |
M |
|
|
201 |
Western Yellow Wagtail Motacilla
flava |
|
|
4 |
|
|
|
202 |
Grey Wagtail Motacilla
cinerea |
|
|
4 |
M |
|
|
203 |
White-browed Wagtail Motacilla
maderaspatensis |
|
|
4 |
R/M |
|
|
204 |
White Wagtail Motacilla alba |
|
|
4 |
M |
|
|
|
52. Fringillidae (finches,
euphonias and Hawaiian honeycreepers) |
|
|
|
|
|
|
205 |
Common Rosefinch Erythrina
erythrina |
|
|
4 |
M |
|
|
|
53. Emberizidae (Old World
buntings) |
|
|
|
|
|
|
206 |
Red-headed Bunting Emberiza
bruniceps |
|
|
4 |
M |
|
|
207 |
Black-headed Bunting Emberiza
melanocephala |
|
|
4 |
M |
|
|
208 |
Grey-necked Bunting Emberiza
buchanani |
|
|
4 |
M |
|
|
|
54. Stenostiridae
(fairy-flycatcher and crested flycatchers) |
|
|
|
|
|
|
209 |
Grey-headed Canary-flycatcher Culicicapa
ceylonensis |
|
|
4 |
M |
|
|
|
55. Paridae (tits, chickadees) |
|
|
|
|
|
|
210 |
Black-lored Tit Machlolophus
xanthogenys |
|
|
4 |
R |
|
|
|
56. Alaudidae (larks) |
|
|
|
|
|
|
211 |
Sykes’s Short-toed Lark Calandrella
dukhunensis |
|
|
4 |
M |
|
|
212 |
Malabar Lark Galerida
malabarica |
|
|
4 |
R |
|
|
|
57. Cisticolidae (cisticolas) |
|
|
|
|
|
|
213 |
Zitting Cisticola Cisticola
juncidis |
|
|
4 |
R |
|
|
214 |
Grey-breasted Prinia Prinia
hodgsonii |
|
|
4 |
R |
|
|
215 |
Ashy Prinia Prinia socialis |
|
|
4 |
R |
|
|
216 |
Plain Prinia Prinia inornata |
|
|
4 |
R |
|
|
217 |
Common Tailorbird Orthotomus
sutorius |
|
|
4 |
R |
|
|
|
58. Locustellidae (bush
warblers) |
|
|
|
|
|
|
218 |
Grasshopper Warbler Locustella
naevia |
|
|
4 |
M |
|
|
|
59. Acrocephalidae (brush, reed
and swamp warblers) |
|
|
|
|
|
|
219 |
Booted Warbler Iduna caligata |
|
|
4 |
M |
|
|
220 |
Sykes's Warbler Iduna rama |
|
|
4 |
M |
X |
|
221 |
Blyth's Reed Warbler Acrocephalus
dumetorum |
|
|
4 |
M |
|
|
222 |
Paddyfield Warbler Acrocephalus
agricola |
|
|
4 |
M |
|
|
223 |
Clamorous Reed Warbler Acrocephalus
stentoreus |
|
|
4 |
R/M |
|
|
|
60. Hirundinidae (swallows) |
|
|
|
|
|
|
224 |
Northern House Martin Delichon
urbicum |
|
|
|
M |
X |
|
225 |
Streak-throated Swallow Petrochelidon
fluvicola |
|
|
|
M |
|
|
226 |
Red-rumped Swallow Cecropis
daurica |
|
|
|
R |
|
|
227 |
Wire-tailed Swallow Hirundo
smithii |
|
|
|
R |
|
|
228 |
Barn Swallow Hirundo rustica |
|
|
|
M |
|
|
229 |
Eurasian Crag Martin Ptyonoprogne
rupestris |
|
|
|
M |
|
|
230 |
Dusky Crag Martin Ptyonoprogne
concolor |
|
|
|
R |
|
|
|
61. Pycnonotidae (bulbuls) |
|
|
|
|
|
|
231 |
Square-tailed Bulbul Hypsipetes
ganeesa |
|
|
4 |
R |
|
|
232 |
Flame-throated Bulbul Pycnonotus
melanicterus gularis |
WG |
|
4 |
R |
|
|
233 |
Red-whiskered Bulbul Pycnonotus
jocosus |
|
|
4 |
R |
|
|
234 |
Red-vented Bulbul Pycnonotus
cafer |
|
|
4 |
R |
|
|
235 |
White-browed Bulbul Pycnonotus
luteolus |
|
|
4 |
R |
|
|
236 |
Grey-headed Bulbul Brachypodius
priocephalus |
WG |
NT |
4 |
R |
|
|
237 |
Yellow-browed Bulbul Acritillas
indica |
|
|
4 |
R |
|
|
|
62. Phylloscopidae (Old World
leaf warblers ) |
|
|
|
|
|
|
238 |
Yellow-browed Warbler Abrornis
inornatus |
|
|
4 |
M |
X |
|
239 |
Sulphur-bellied Warbler Phylloscopus
griseolus |
|
|
4 |
M |
|
|
240 |
Tickell's Leaf Warbler Phylloscopus
affinis |
|
|
4 |
M |
|
|
241 |
Green Leaf Warbler Seicercus
nitidus |
|
|
4 |
M |
|
|
242 |
Greenish Leaf Warbler Seicercus
trochiloides |
|
|
4 |
M |
|
|
243 |
Large-billed Leaf Warbler Seicercus
magnirostris |
|
|
4 |
M |
|
|
244 |
Western Crowned Leaf Warbler Seicercus
occipitalis |
|
|
4 |
M |
|
|
|
63. Sylviidae (Sylvia warblers,
parrotbills and allies) |
|
|
|
|
|
|
245 |
Yellow-eyed Babbler Chrysomma
sinense |
|
|
4 |
R |
|
|
|
64. Zosteropidae (white-eyes and
yuhinas) |
|
|
|
|
|
|
246 |
Oriental White-eye Zosterops
palpebrosus |
|
|
4 |
R |
|
|
|
65. Timaliidae (scimitar
babblers and allies) |
|
|
|
|
|
|
247 |
Indian Scimitar Babbler Pomatorhinus
horsfieldii |
|
|
4 |
R |
|
|
248 |
Tawny-bellied Babbler Dumetia
hyperythra albogularis |
|
|
4 |
R |
|
|
249 |
Dark-fronted Babbler Rhopocichla
atriceps |
|
|
4 |
R |
|
|
250 |
Puff-throated Babbler Pellorneum
ruficeps |
|
|
4 |
R |
|
|
|
66. Pellorneidae (smaller
babblers) |
|
|
|
|
|
|
251 |
Quaker Tit Babbler Alcippe
poioicephala |
|
|
4 |
R |
|
|
|
67. Leiothrichidae (babblers,
laughingthrushes and allies) |
|
|
|
|
|
|
252 |
Rufous Babbler Argya subrufa |
WG |
|
4 |
R |
|
|
253 |
Jungle (Black-winged) Babbler Turdoides
striata somervillei |
WG |
|
4 |
R |
|
|
254 |
Yellow-billed Babbler Turdoides
affinis |
|
|
4 |
S |
X |
|
255 |
Waynaad Laughingthrush Garrulax
delesserti |
WG |
|
4 |
R |
|
|
|
68. Sittidae (nuthatches,
spotted creepers and wallcreeper) |
|
|
|
|
|
|
256 |
Velvet-fronted Nuthatch Sitta
frontalis |
|
|
|
R |
|
|
|
69. Sturnidae (starlings) |
|
|
|
|
|
|
257 |
Rosy Starling Pastor roseus |
|
|
4 |
M |
|
|
258 |
Brahminy Starling Sturnia
pagodarum |
|
|
4 |
R |
|
|
259 |
Chestnut-tailed Starling Sturnia
malabarica |
|
|
4 |
R |
|
|
260 |
Malabar Starling Sturnia
malabarica blythii |
WG |
|
4 |
R |
|
|
261 |
Common Myna Acridotheres
tristis |
|
|
4 |
R |
|
|
262 |
Jungle Myna Acridotheres
fuscus |
|
|
4 |
R |
|
|
263 |
Southern Hill Myna Gracula
indica |
|
|
1 |
R |
|
|
|
70. Muscicapidae (chats ad
flycatchers) |
|
|
|
|
|
|
264 |
Indian Robin Saxicoloides
fulicatus |
|
|
4 |
R |
|
|
265 |
Oriental Magpie Robin Copsychus
saularis |
|
|
4 |
R |
|
|
266 |
White-rumped Shama Kittacincla
malabarica |
|
|
4 |
R |
|
|
267 |
Dark-sided Flycatcher Muscicapa
sibirica § |
|
|
4 |
VG |
X |
|
268 |
Asian Brown Flycatcher Muscicapa
dauurica |
|
|
4 |
M |
|
|
269 |
Brown-breasted Flycatcher Muscicapa
muttui |
|
|
4 |
M |
|
|
270 |
Rusty-tailed Flycatcher Muscicapa
ruficauda |
|
|
4 |
M |
|
|
271 |
White-bellied Blue Flycatcher Cyornis
pallidipes |
WG |
|
4 |
R |
|
|
272 |
Tickell's Blue Flycatcher Cyornis
tickelliae |
|
|
4 |
R |
|
|
273 |
Verditer Flycatcher Eumyias
thalassinus |
|
|
4 |
M |
|
|
274 |
Indian Blue Robin Larvivora
brunnea |
|
|
4 |
M |
|
|
275 |
Malabar Whistling Thrush Myophonus
horsfieldii |
|
|
4 |
R |
|
|
276 |
Red-breasted Flycatcher Ficedula
parva |
|
|
4 |
M |
|
|
277 |
Taiga Flycatcher Ficedula
albicilla |
|
|
4 |
M |
|
|
278 |
Ultramarine Flycatcher Ficedula
superciliaris |
|
|
4 |
M |
X |
|
279 |
Black Redstart Phoenicurus
ochruros |
|
|
4 |
M |
X |
|
280 |
Blue-capped Rock Thrush Monticola
cinclorhyncha |
|
|
4 |
M |
|
|
281 |
Blue Rock Thrush Monticola
solitarius |
|
|
4 |
M |
|
|
282 |
Siberian Stonechat Saxicola
maurus |
|
|
4 |
M |
|
|
283 |
Pied Bushchat Saxicola caprata |
|
|
4 |
R |
|
|
|
71. Turdidae (thrushes) |
|
|
|
|
|
|
284 |
Orange-headed Thrush Geokichla
citrina |
|
|
4 |
|
|
|
285 |
Indian Blackbird Turdus
simillimus |
|
|
4 |
R |
|
|
286 |
Tickell's Thrush Turdus
unicolor |
|
|
4 |
M |
X |
Appendix
II. Wild Angiosperms of Bhagwan Mahavir National Park, Goa, India (adapted from
Datar & Lakshminarasimhan 2013).
Abbreviations
used for endemism: WG—Western Ghats | PI—peninsular India | AN—Andaman &
Nicobar Islands | IND—India | SWI—southwestern India | NWG—northern Western
Ghats | WI—western India | WSI—western and southern India | PCI—peninsular and
central India | WPI—western peninsular India | Goa—Goa state.
Abbreviations used for Red Listed Species:
CR—Critically Endangered | EN—Endangered | VU—Vulnerable
|
Species
/ Family |
Local
name |
Endemism |
Iucn |
|
ACANTHACEAE |
|
|
|
|
Andrographis
paniculata (Burm.f.) Wall. ex Nees |
Chirayat |
|
|
|
Asystasia
dalzelliana Santapau |
|
Endemic
WG |
|
|
Barleria
prattensis Santapau |
|
|
|
|
Barleria
prionitis L. |
|
|
|
|
Barleria
terminalis Nees |
|
|
|
|
Cynarospermum
asperrimum (Nees) Vollesen |
|
Endemic
PCI |
|
|
Dicliptera
foetida (Forssk.) Blatt. |
|
|
|
|
Ecbolium
ligustrinum (Vahl) Vollesen |
|
|
|
|
Eranthemum
capense L. var. concanensis (T.Anderson
ex C. B. Clarke) Santapau |
|
Endemic
WG |
VU |
|
Eranthemum
roseum (Vahl) R.Br. |
|
Endemic
WG |
|
|
Gymnostachyum
glabrum (Dalzell) T.Anderson |
|
|
|
|
Haplanthodes
tentaculatus (L.) R.B.Majumdar |
|
|
|
|
Hemigraphis
latebrosa (B.Heyne ex Roth) Nees |
|
|
|
|
Hygrophila
pinnatifida (Dalzell) Sreem. |
|
|
|
|
Hygrophila
ringens (L.) R.Br. ex Steud. |
|
|
|
|
Hygrophila
schulli (Buch.-Ham.) M.R.Almeida &
S.M.Almeida |
|
|
|
|
Justicia
adhatoda L. |
Adulsa |
|
|
|
Justicia
procumbens L. |
|
|
|
|
Justicia
simplex D.Don |
|
|
|
|
Justicia
wynaadensis (Nees) Heyne ex T.Anderson |
|
Endemic
WG |
|
|
Lepidagathis
cuspidata Nees |
|
|
|
|
Lepidagathis
incurva Buch.-Ham. ex D.Don var. mucronata
(Nees) C.B.Clarke ex T.Cooke |
|
|
|
|
Lepidagathis
lutea Dalzell |
Koche |
|
|
|
Lepidagathis
prostrata Dalzell |
|
|
|
|
Nelsonia
canescens (Lam.) Spreng. |
|
|
|
|
Phaulopsis
imbricata (Forssk.) Sweet |
|
|
|
|
Pseuderanthemum
malabaricum (C.B.Clarke) Gamble |
|
|
|
|
Rostellularia
japonica (Thunb.) Ellis |
|
|
|
|
Rungia
parviflora (Retz.) Nees ssp. pectinata (L.)
L.H.Cramer |
|
|
|
|
Strobilanthes
callosus Nees |
Karaw |
Endemic
WI |
|
|
Strobilanthes
ciliata Nees |
|
Endemic
WG |
EN |
|
Strobilanthes
heyneanus Nees |
Karaw |
Endemic
PI |
|
|
Strobilanthes
integrifolia (Dalzell) Kuntze |
|
Endemic
WG |
|
|
Strobilanthes
ixiocephalus Benth. |
Kaarw |
Endemic
WG |
|
|
ALISMATACEAE |
|
|
|
|
Wiesneria
triandra (Dalzell) Micheli |
|
|
EN |
|
AMARANTHACEAE |
|
|
|
|
Achyranthes
aspera L. |
|
|
|
|
Alternanthera
sessilis (L.) R.Br. ex DC. |
|
|
|
|
Amaranthus
spinosus L. |
|
|
|
|
Celosia
argentea L. |
|
|
|
|
Cyathula
prostrata (L.) Blume |
|
|
|
|
AMARYLLIDACEAE |
|
|
|
|
Crinum
lorifolium Roxb. ex Ker Gawl. |
|
|
|
|
Crinum
viviparum (Lam.) R.Ansari & V.J.Nair |
|
|
|
|
Pancratium
triflorum Roxb. |
|
|
|
|
ANACARDIACEAE |
|
|
|
|
Anacardium
occidentale L. |
Kaju |
|
|
|
Buchanania
lanzan Spreng. |
Char |
|
|
|
Holigarna
arnottiana Hook.f. |
Bibba |
Endemic
WG |
|
|
Holigarna
grahamii (Wight) Kurz |
|
Endemic
WG |
|
|
Lannea
coromandelica (Houtt.) Merr. |
|
|
|
|
Mangifera
indica L. |
Amba |
|
|
|
Nothopegia
beddomei Gamble |
|
Endemic
WG |
|
|
Nothopegia
castaneifolia (Roth) Ding Hou |
|
Endemic
WG |
|
|
ANCISTROCLADACEAE |
|
|
|
|
Ancistrocladus
heyneanus Wall. ex J.Graham |
|
Endemic
WG |
|
|
ANNONACEAE |
|
|
|
|
Miliusa
tomentosa (Roxb.) Finet and Gagnep. |
|
|
|
|
Orophea
zeylanica Hook.f. & Thomson |
|
|
|
|
Polyalthia
fragrans (Dalzell) Bedd. |
|
Endemic
WG |
|
|
Sageraea
laurina Dalzell |
Sadni |
Endemic
WG |
|
|
Uvaria
narnum (Dunal) Blume |
|
|
|
|
ANTHERICACEAE |
|
|
|
|
Chlorophytum
heynei Rottl. ex Baker |
|
|
|
|
APIACEAE |
|
|
|
|
Centella
asiatica (L.) Urb. |
|
|
|
|
Pimpinella
wallichiana (Miq. ex Hohen.) Gandhi |
|
|
|
|
APOCYNACEAE: SUBFAMILY ASCLEPIADOIDEAE |
|
|
|
|
Asclepias
curassavica L. |
|
|
|
|
Calotropis
gigantea (L.) R.Br. |
|
|
|
|
Cynanchum
callialata Buch.-Ham. ex Wight |
|
|
|
|
Dregea
volubilis (L. f.) Benth. ex Hook.f. |
|
|
|
|
Genianthus
laurifolius (Roxb.) Hook.f. |
|
|
|
|
Gymnema
sylvestre (Retz.) R.Br. ex Schult. |
|
|
|
|
Holostemma
annulare (Roxb.) K.Schum. |
|
|
|
|
Hoya
wightii Hook.f. |
|
Endemic
PI |
|
|
Tylophora
fasciculata Buch.-Ham. ex Wight & Arn. |
|
|
|
|
APOCYNACEAE: SUBFAMILY APOCYNOIDEAE |
|
|
|
|
Aganosma
cymosa (Roxb.) G.Don |
|
|
|
|
Anodendron
paniculatum (Roxb.) A.DC. |
|
|
|
|
Chonemorpha
fragrans (Moon) Alston |
|
|
|
|
Holarrhena
pubescens (Buch.- Ham) Wall. ex G.Don |
|
|
|
|
Ichnocarpus
frutescens (L.) W.T.Aiton |
|
|
|
|
Parsonsia
alboflavescens (Dennst.) Mabb. |
|
|
|
|
Wrightia
arborea (Dennst.) Mabb. |
|
|
|
|
Wrightia
tinctoria (Roxb.) R.Br. |
|
|
|
|
APOCYNACEAE: SUBFAMILY- RAUVOLFIOIDEAE |
|
|
|
|
Alstonia
scholaris (L.) R.Br. |
|
|
|
|
Carissa
spinarum L. |
|
|
|
|
Rauvolfia
serpentina (L.) Benth. ex Kurz |
|
|
|
|
Tabernaemontana
alternifolia L. |
|
Endemic
WSI |
|
|
APOCYNACEAE: SUBFAMILY PERIPLOCOIDEAE |
|
|
|
|
Cryptolepis
buchananii R.Br. ex Roem. & Schult. |
|
|
|
|
Hemidesmus
indicus (L.) R.Br. |
|
|
|
|
ARACEAE |
|
|
|
|
Amorphophallus
bulbifer (Roxb.) Blume |
|
|
|
|
Amorphophallus
commutatus (Schott) Engl. var. commutatus |
|
Endemic
PI |
|
|
Amorphophallus
commutatus var. anmodensis Sivad. &
Jaleel |
|
Endemic
Goa |
EN |
|
Amorphophallus
paeoniifolius (Dennst.) Nicolson |
|
|
|
|
Ariopsis
peltata Nimmo |
|
|
|
|
Arisaema
sivadasanii S.R.Yadav, K.S.Patil & Janarth. |
|
Endemic
WG |
CR |
|
Arisaema
tortuosum (Wall.) Schott |
|
|
|
|
Cryptocoryne
retrospiralis (Roxb.) Kunth |
|
|
|
|
Lagenandra
ovata (L.) Thwaites |
|
|
|
|
Pothos
scandens L. |
|
|
|
|
Theriophonum
dalzelli Schott. |
|
Endemic
WG |
|
|
ARALIACEAE |
|
|
|
|
Schefflera
elliptica (Blume) Harms |
|
|
|
|
ARECACEAE |
|
|
|
|
Arenga
wightii Griff |
|
Endemic WG |
|
|
Calamus
pseudotenuis Becc. |
Wet |
|
|
|
Calamus
thwaitesii Becc. |
Wet |
|
|
|
Caryota
urens L. |
Bherli mad |
|
|
|
ARISTROLOCHIACEAE |
|
|
|
|
Thottea
siliquosa (Lam.) Ding Hou |
|
|
|
|
ASPARAGACEAE |
|
|
|
|
Asparagus
racemosus Willd. |
|
|
|
|
ASTERACEAE |
|
|
|
|
Acanthospermum
hispidum DC. |
|
|
|
|
Ageratum
conyzoides L. |
|
|
|
|
Bidens
biternata (Lour.) Merr. & Sherff |
|
|
|
|
Blumea
belangeriana DC. |
|
Endemic PI |
|
|
Blumea
membranacea DC. |
|
|
|
|
Blumea
oxyodonta DC. |
|
|
|
|
Blumea
virens DC. |
|
|
|
|
Cyathocline
purpurea (Buch.-Ham. ex D.Don) Kuntze |
|
|
|
|
Dichrocephala
integrifolia (L.f.) Kuntze |
|
|
|
|
Eclipta
prostrata (L.) L. |
|
|
|
|
Elephantopus
scaber L. |
|
|
|
|
Emilia
sonchifolia (L.) DC. |
|
|
|
|
Erigeron
sublyratus DC. |
|
|
|
|
Eupatorium
odoratum L. |
|
|
|
|
Gnaphalium
polycaulon Pers. |
|
|
|
|
Grangea
maderaspatana (L.) Poir. |
|
|
|
|
Gynura
nitida DC. |
|
|
|
|
Phyllocephalum
phyllolaenum (DC.) Narayana |
|
|
|
|
Phyllocephalum
ritchiei (Hook.f.) Narayana |
|
Endemic PI |
|
|
Senecio
belgaumensis (Wight) C.B.Clarke |
|
|
|
|
Senecio
gibsonii Hook.f. |
|
Endemic WG |
|
|
Spilanthes
paniculata Wall. ex DC. |
|
|
|
|
Synedrella
nodiflora (L.) Gaertn. |
|
|
|
|
Tricholepis
glaberrima DC. |
|
|
|
|
Tridax
procumbens L. |
|
|
|
|
Vernonia
cinerea (L.) Less. |
|
|
|
|
BALSAMINACEAE |
|
|
|
|
Impatiens
acaulis Arn. |
|
|
|
|
Impatiens
balsamina L. |
Terda |
|
|
|
Impatiens
lawii Hook.f. & Thomson |
|
|
|
|
Impatiens
minor (DC.) Bennet |
|
Endemic WG |
|
|
Impatiens
oppositifolia L. |
|
|
|
|
Impatiens
pulcherrima Dalzell |
|
Endemic WG |
|
|
BEGONIACEAE |
|
|
|
|
Begonia
crenata Drynad. |
|
|
|
|
Begonia
trichocarpa Dalzell |
|
Endemic NWG |
EN |
|
BIGNONIACEAE |
|
|
|
|
Heterophragma
quadriloculare (Roxb.) K.Schum. |
Kuski |
|
|
|
Oroxylum
indicum (L.) Benth. ex Kurz |
|
|
|
|
Pajanelia
longifolia (Willd.) K.Schum. |
Padwal |
|
|
|
Stereospermum
colais (Buch.-Ham. ex Dillw.) Mabb. |
|
|
|
|
BOMBACACEAE |
|
|
|
|
Bombax
ceiba L. |
Sawar |
|
|
|
Bombax
insigne Wall. |
|
|
|
|
BORAGINACEAE |
|
|
|
|
Coldenia
procumbens L. |
|
|
|
|
Cynoglossum
zeylanicum (Vahl ex Hornem.) Thunb. ex Lehm. |
|
|
|
|
Ehretia
canarensis (C.B.Clarke) Gamble |
|
|
|
|
Paracaryopsis
coelestina (Lindl.) R.R.Mill |
|
|
VU |
|
Rotula
aquatica Lour. |
|
|
|
|
BUDDLEJACEAE |
|
|
|
|
Buddleja
asiatica Lour. |
|
|
|
|
BURMANNIACEAE |
|
|
|
|
Burmannia
pusilla (Wall. ex Miers) Thwaites |
|
|
|
|
BURSERACEAE |
|
|
|
|
Canarium
strictum Roxb. |
Dhup |
|
|
|
CAMPANULACEAE |
|
|
|
|
Lobelia
alsinoides Lam. |
|
|
|
|
Lobelia
nicotianaefolia Roth ex Roem. &
Schult. |
Rantambaku |
|
|
|
CAPPARACEAE |
|
|
|
|
Capparis
rheedei DC. |
|
Endemic WG |
|
|
Cleome
viscosa L. |
|
|
|
|
CARYOPHYLLACEAE |
|
|
|
|
Polycarpon
prostratum (Forssk.) Asch. & Schweinf. |
|
|
|
|
CELASTRACEAE |
|
|
|
|
Celastrus
paniculata Willd |
|
|
|
|
Euonymus
indicus B. Heyne ex Wall. |
|
Endemic PI & AN |
|
|
Hippocratea
grahamii Wight |
|
|
|
|
Hippocratea
indica Willd. |
|
|
|
|
Hippocratea
obtusifolia Roxb. |
|
|
|
|
Lophopetalum
wigtianum Arn. |
|
|
|
|
Maytenus
rothiana (Walp.) Lobreau-Callen |
|
|
|
|
Salacia
chinensis L. |
Narbundi |
|
|
|
Salacia
oblonga Wall ex Wight & Arn. |
|
|
|
|
CLEOMACEAE |
|
|
|
|
Crateva
magna (Lour.) DC. |
|
|
|
|
CLUSIACEAE |
|
|
|
|
Calophyllum
calaba L. |
Wiray |
Endemic
WG |
|
|
Calophyllum
polyanthum Wall. ex Choisy |
|
|
|
|
Garcinia
gummi-gutta (L.) N.Robson |
|
Endemic
WG |
|
|
Garcinia
indica (Thouars ) Choisy |
Bhirand, Kokam, Aamsul |
Endemic
WG |
|
|
Garcinia
morella (Gaertn.) Desr. |
|
|
|
|
Mammea
suriga (Buch.-Ham. ex Roxb.) Kosterm. |
Surangi |
|
|
|
Mesua
ferrea L. |
Nag-Chapha |
|
|
|
COLCHICACEAE |
|
|
|
|
Gloriosa
superba L. |
|
|
|
|
Iphiginea
indica (L.) A. Grey ex Kunth |
|
|
|
|
COMBRETACEAE |
|
|
|
|
Combretum
latifolium Blume |
|
|
|
|
Getonia
floribunda Roxb. |
Uski |
|
|
|
Terminalia
bellirica (Gaertn.) Roxb. |
|
|
|
|
Terminalia
chebula Retz. |
|
|
|
|
Terminalia
elliptica Willd. |
Matti, Madat |
|
|
|
Terminalia
paniculata Roth |
Kindal |
Endemic PI |
|
|
COMMELINACEAE |
|
|
|
|
Commelina
benghalensis L. |
|
|
|
|
Commelina
forsskalaei Vahl |
|
|
|
|
Cyanotis
fasciculata (B.Heyne ex Roth) Schult. &
Schult.f. |
|
|
|
|
Cynotis
cristata (L.) D.Don |
|
|
|
|
Floscopa
scandens Lour. |
|
|
|
|
Murdannia
dimorpha (Dalzell) G.Brückn. |
|
|
|
|
Murdannia
japonica (Thunb.) Faden |
|
|
|
|
Murdannia
semiteres (Dalzell) Santapau |
|
|
|
|
Murdannia
simplex (Vahl) Brenan |
|
|
|
|
Murdannia
spirata (L.) G.Brückn. |
|
|
|
|
Murdannia
versicolor (Dalzell) G.Brückn. |
|
|
|
|
CONNARACEAE |
|
|
|
|
Connarus
monocarpus L. |
Ghagrya |
|
|
|
CONVALLARIACEAE |
|
|
|
|
Ophiopogon
intermedius D.Don |
|
|
|
|
CONVOLVULACEAE |
|
|
|
|
Argyreia
elliptica (Roth) Choisy |
|
|
|
|
Argyreia
involucrata C.B.Clarke |
|
|
|
|
Erycibe
paniculata Roxb. |
|
|
|
|
Evolvulus
nummularius (L.) L. |
|
|
|
|
Ipomoea
campanulata L. |
|
|
|
|
Ipomoea
nil (L.) Roth |
|
|
|
|
Ipomoea
obscura (L.) Ker Gawl. |
|
|
|
|
Ipomoea
sinensis (Desv.) Choisy |
|
|
|
|
Ipomoea
violacea L. |
|
|
|
|
Merremia
umbellata (L.) Hall f. |
Washel |
|
|
|
Merremia
vitifolia (Burm.f.) Hall f. |
|
|
|
|
CORNACEAE |
|
|
|
|
Mastixia
arborea (Wight.) Bedd. |
|
|
|
|
COSTACEAE |
|
|
|
|
Costus
speciosus (J.J.König) J.E.Sm. |
|
|
|
|
CRASSULACEAE |
|
|
|
|
Kalanchoe
pinnata (Lam.) Pers. |
|
|
|
|
CUCURBITACEAE |
|
|
|
|
Coccinia
grandis (L.) Voigt |
Tendli |
|
|
|
Cucumis
melo L. |
|
|
|
|
Momordica
dioica Roxb. ex Willd. |
|
|
|
|
Mukia
maderaspatana (L.) M.Roem. |
|
|
|
|
Solena
amplexicaulis (Lam.) Gandhi |
|
|
|
|
Trichosanthes
cucumerina L. |
Kondal,
Fagal |
|
|
|
Zanonia
indica L. |
|
|
|
|
CYPERACEAE |
|
|
|
|
Carex
caricina (D.Don) Ghildyal & U.C.Bhattach.
var. caricina. |
|
|
|
|
Carex
caricina (D.Don) Ghildyal & U.C.Bhattach.
var. glaucina (Boeck.) Ghildyal & U.C.Bhattach. |
|
Endemic
PI |
|
|
Cyperus
haspan L. ssp. haspan. |
|
|
|
|
Cyperus
haspan L. ssp. juncoides (Lam.) Kuk. |
|
|
|
|
Cyperus
iria L. |
|
|
|
|
Diplacrum
caricinum R.Br. |
|
|
|
|
Eleocharis
acutangula (Roxb.) Schult. |
|
|
|
|
Fimbristylis
dichotoma (L.) Vahl |
|
|
|
|
Fimbristylis
lawiana (Boeck.) J.Kern |
|
|
|
|
Fimbristylis
ovata (Burm.f.) J.Kern |
|
|
|
|
Fimbristylis
woodrowii C.B.Clarke |
|
Endemic
WPI |
|
|
Hypolytrum
nemorum (Vahl) Spreng. |
|
|
|
|
Kyllinga
brevifolia Rottb. |
|
|
|
|
Lipocarpha
squarrosa (L.) Goetgh. |
|
|
|
|
Mariscus
compactus (Retz.) Bold. |
|
|
|
|
Mariscus
paniceus (Rottb.) Vahl |
|
|
|
|
Pycreus
flavidus (Retz.) T.Koyma |
|
|
|
|
Pycreus
malabaricus C.BClarke |
|
|
|
|
Pycreus
pumilus (L.) Nees |
|
|
|
|
Pycreus
sanguinolentus (Vahl) Nees |
|
|
|
|
Rhynchospora
wightiana (Nees) Steud. |
|
|
|
|
Scleria
terrestris (L.) Fassett |
|
|
|
|
DATISCACEAE |
|
|
|
|
Tetrameles
nudiflora R. Br. |
|
|
|
|
DILLENIACEAE |
|
|
|
|
Dillenia
pentagyna Roxb. |
Karmal |
|
|
|
DIOSCOREACEAE |
|
|
|
|
Dioscorea
bulbifera L. |
|
|
|
|
Dioscorea
hispida Dennst. |
|
|
|
|
Dioscorea
pentaphylla L. |
|
|
|
|
DIPTEROCARPACEAE |
|
|
|
|
Hopea
ponga (Dennst.) Mabb. |
|
Endemic WG |
|
|
DRACAENACEAE |
|
|
|
|
Dracaena
terniflora Roxb. |
|
|
|
|
DROSERACEAE |
|
|
|
|
Drosera
indica L. |
|
|
|
|
EBENACEAE |
|
|
|
|
Diospyros
buxifolia (Blume) Hiern |
|
|
|
|
Diospyros
candolleana Wight |
|
|
|
|
Diospyros
crumenata Thwaites |
|
|
|
|
Diospyros
montana Roxb. |
Kalakonda |
|
|
|
Diospyros
neilgerrensis (Wight) Kosterm. |
|
Endemic PI |
|
|
Diospyros
oocarpa Thw. |
|
|
|
|
Diospyros
paniculata Dalzell |
|
Endemic IND |
|
|
Diospyros
pruriens Dalzell |
|
|
|
|
ELAEAGNACEAE |
|
|
|
|
Elaeagnus
conferta Roxb. |
|
|
|
|
ERIOCAULACEAE |
|
|
|
|
Eriocaulon
dalzellii Koern. |
|
Endemic WG |
|
|
Eriocaulon
eurypeplon Koern. |
|
Endemic WG |
|
|
Eriocaulon
heterolepis Steud. |
|
Endemic WI |
|
|
Eriocaulon
lanceolatum Miq. ex Koern. |
|
Endemic WG |
|
|
Eriocaulon
robusto-brownianum Ruhland |
|
|
|
|
Eriocaulon
sexangulare L. |
|
|
|
|
Eriocaulon
stellulatum Koern. |
|
Endemic WG |
|
|
Eriocaulon
xeranthemum Mart. |
|
|
|
|
Eroicaulon
palghatense R.Ansari & N.P.Balakr. |
|
Endemic WG |
|
|
EUPHORBIACEAE
s.l. |
|
|
|
|
Actephila
excelsa (Dalzell) Mull. Arg. |
|
|
|
|
Agrostistachys
indica Dalzell |
|
|
|
|
Antidesma
acidum Retz. |
|
|
|
|
Antidesma
menasu (Tul.) Mull. Arg. |
|
|
|
|
Aporusa
cardiosperma (Gaertn.) Merr. |
|
|
|
|
Baliospermum
montanum (Willd.) Mull. Arg. |
|
|
|
|
Blachia
andamanica (Kurz) Hook.f. ssp. denudata (Benth.)
N.P.Balakr. & Chakrab. |
|
Endemic WG |
|
|
Breynia
retusa (Dennst.) Alston |
|
|
|
|
Bridelia
retusa (L.) A.Juss. |
|
|
|
|
Bridelia
stipularis Blume |
|
|
|
|
Croton
persimilis Mull. Arg. |
|
|
|
|
Dimorphocalyx
glabellus Thwaites var. lawianus (Mull.
Arg.) Chakrab. & N.P.Balakr. |
|
Endemic WG |
|
|
Drypetes
venusta (Wight) Pax & K.Hoffm. |
|
|
|
|
Euphorbia
erythroclada Boiss |
|
Endemic PCI |
|
|
Euphorbia
hirta L. |
|
|
|
|
Euphorbia
ligularia Roxb. |
|
|
|
|
Euphorbia
notoptera Boiss. |
|
Endemic WG |
|
|
Falconeria
insignis Royle |
|
|
|
|
Glochidion
hohenackeri (Mull.-Arg.) Bedd. |
|
Endemic NWG |
|
|
Glochidion
zeylanicum (Gaertn.) A.Juss. |
|
|
|
|
Homonoia
riparia Lour. |
|
|
|
|
Jatropha
curcas L. |
|
|
|
|
Macaranga
peltata (Roxb.) Mull. Arg. |
Chanda |
|
|
|
Mallotus
ferrugineus (Roxb.) Mull. Arg. |
|
|
|
|
Mallotus
philippensis (Lam.) Mull. Arg. |
|
|
|
|
Mallotus
resinous (Blanco) Merr. var. stenanthus (Mull.
Arg.) Susila & N.P.Balakr. |
|
Endemic
WG |
|
|
Margaritaria
indica (Dalzell) Airy Shaw |
|
|
|
|
Microstachys
chamaelea (L.) Mull. Arg. |
|
|
|
|
Phyllanthus
amarus Schumach. & Thonn. |
|
|
|
|
Phyllanthus
emblica L. |
Awla |
|
|
|
Phyllanthus
juniperinus Mull. Arg. |
|
|
|
|
Phyllanthus
simplex Retz. |
|
|
|
|
Phyllanthus
urinaria L. |
|
|
|
|
Tragia
praetervis Chakrab. & N.P.Balakr. |
|
|
|
|
FLACOURTIACEAE |
|
|
|
|
Casearia
ovata (Lam.) Willd. |
|
|
|
|
Flacourtia
montana J.Graham |
Chaper |
Endemic
WG |
|
|
Homalium
ceylanicum (Gardn.) Benth. |
|
|
|
|
Hydnocarpus
pentandrus (Buch.-Ham.) Oken |
Kastal |
Endemic
WG |
|
|
GENTIANACEAE |
|
|
|
|
Canscora
diffusa (Vahl) R.Br. ex Roem &
Schult. |
|
|
|
|
Canscora
perfoliata Lam. |
|
Endemic
WG |
|
|
Exacum
pumilum Griseb. |
|
|
|
|
Exacum
tetragonum Roxb. |
|
|
|
|
Hoppea
fastigiata (Griseb.) C.B.Clarke |
|
|
|
|
GESNERIACEAE |
|
|
|
|
Rhynchoglossum
notonianum (Wall.) Burtt |
|
|
|
|
Rhynchoglossum
obliquum Blume var. parviflorum C.B.Clarke |
|
|
|
|
HYCINTHACEAE |
|
|
|
|
Ledebouria
revoluta (L.f.) Jessop |
|
|
|
|
HYDROCHARITACEAE |
|
|
|
|
Blyxa
aubertii Rich. |
|
|
|
|
Vallisneria
spiralis L. |
|
|
|
|
HYACINTHACEAE |
|
|
|
|
Curculigo
orchioides Gaertn. |
|
|
|
|
ICACINACEAE |
|
|
|
|
Gomphandra
tetrandra (Wall.) Sleumer |
|
|
|
|
Nothapodytes
nimmoniana (J. Graham) Mabb. |
|
|
|
|
Sarcostigma
kleinii Wight & Arn. |
|
|
|
|
LAMIACEAE |
|
|
|
|
Anisomeles
indica (L.) Kuntze |
|
Endemic
WG |
|
|
Callicarpa
tomentosa (L.) L. |
|
|
|
|
Clerodendrum
infortunatum L. |
|
|
|
|
Colebrookea
oppositifolia Sm. |
|
|
|
|
Gmelina
arborea Roxb. |
Shiwan |
|
|
|
Hyptis
capitata Jacq. |
|
|
|
|
Hyptis
suaveolens (L.) Poit. |
|
|
|
|
Leucas
biflora (Vahl) R. Br. ex Sm. |
|
|
|
|
Leucas
ciliata Benth. |
|
|
|
|
Leucas
lavendulifolia Sm. |
|
|
|
|
Leucas
stelligera Wall. |
|
|
|
|
Platostoma
hispidum (L.) A.J.Paton |
|
|
|
|
Pogostemon
paniculatus (Willd.) Benth |
|
|
|
|
Pogostemon
purpurascens Dalzell |
|
|
|
|
Premna
coriacea C.B.Clarke |
|
|
|
|
Rotheca
serrata (L.) D.A.Steane & Mabb. |
|
|
|
|
Scutellaria
discolor Colebr. |
|
|
|
|
Tectona
grandis L.f. |
Sagon |
|
|
|
Vitex
altissima L.f. |
Bailado |
|
|
|
Vitex
leucoxylon L.f. |
|
|
|
|
Vitex
negundo L. |
|
|
|
|
LAURACEAE |
|
|
|
|
Actinodaphne
angustifolia (Blume) Nees |
|
|
|
|
Beilschmiedia
dalzellii (Meisn.) Kosterm. |
Miryo |
|
|
|
Cinnamomum
nitidum (Roxb.) Hook. |
|
|
|
|
Cinnamomum
sulphuratum Nees |
Tikki |
|
|
|
Cinnamomum
verum J.Presl |
Tikki |
|
|
|
Cryptocarya
lawsonii Gamble |
|
Endemic
WG |
|
|
Litsea
coriacea (Heyne ex Meisn.) Hook.f. |
|
Endemic
WG |
|
|
Litsea
ghatica C.J.Saldanha |
|
Endemic
WG |
|
|
Persea
macrantha (Nees) Kosterm. |
Olamb |
|
|
|
LECYTHIDACEAE |
|
|
|
|
Careya
arborea Roxb. |
Kumyo |
|
|
|
LEEACEAE |
|
|
|
|
Leea
asiatica (L.) Ridsdale |
|
|
|
|
Leea
indica (Burm.f.) Merr. |
Dino |
|
|
|
LEGUMINOSAE: SUBFAMILY CAESALPINIOIDEAE |
|
|
|
|
Bauhinia
malabarica Roxb. |
|
|
|
|
Bauhinia
racemosa Lam. |
Apto |
|
|
|
Caesalpinia
mimosoides Lam. |
Pansi |
|
|
|
Cassia
fistula L. |
Bayo |
|
|
|
Chamaecrista
absus (L.) H.S.Irwin & Barneby |
|
|
|
|
Moullava
spicata (Dalzell) Nicolson |
Shamachi Wal |
Endemic
PI |
|
|
Saraca
asoca (Roxb.) W.J.de Wilde |
Ashok |
|
|
|
Senna
hirsuta (L.) H.S.Irwin & Barneby |
Taykolo |
|
|
|
Senna
obtusifolia (L.) H.S.Irwin & Barneby |
|
|
|
|
Senna
tora (L.) Roxb. |
|
|
|
|
LEGUMINOSAE: SUBFAMILY MIMOSOIDEAE |
|
|
|
|
Acacia
caesia (L.) Willd. |
|
|
|
|
Acacia
chundra (Roxb. & Rottl.) Willd. |
|
|
|
|
Acacia
concinna (Willd.) DC. |
Shikekai |
|
|
|
Acacia
pennata (L.) Willd. |
|
|
|
|
Acacia
torta (Roxb.) Craib. |
|
|
|
|
Albizia
chinensis (Osbeck.) Merr. |
|
|
|
|
Albizia
odoratissima (L.f.) Benth. |
|
|
|
|
Entada
rheedei Spreng. |
Garmbi |
|
|
|
Mimosa
pudica L. |
|
|
|
|
Xylia
xylocarpa (Roxb.) Taub. |
Jambha |
|
|
|
LEGUMINOSAE: SUBFAMILY PAPILIONOIDEAE |
|
|
|
|
Abrus
pulchellus Wall. ex Thwaites |
Gunj |
|
|
|
Aeschynomene
indica L. |
|
|
|
|
Alysicarpus
bupleurifolius (L.) DC. |
|
|
|
|
Alysicarpus
glumaceus (Vahl.) DC. |
|
|
|
|
Butea
monosperma (Lam.) Taub. |
Palas |
|
|
|
Cajanus
lineatus (Wight & Arn.) Maesen |
|
|
|
|
Crotalaria
filipes Benth. |
|
Endemic
WG |
|
|
Crotalaria
lutescens Dalzell |
|
Endemic
WG |
|
|
Crotalaria
pallida Aiton |
|
|
|
|
Crotalaria
prostrata Rottl. |
|
|
|
|
Crotalaria
retusa L. |
|
|
|
|
Dalbergia
horrida (Dennst.) Mabb. |
|
Endemic
WG |
|
|
Dalbergia
latifolia Roxb. |
Sisam |
|
|
|
Dalbergia
rubiginosa Roxb. |
|
Endemic
PI |
|
|
Dendrolobium
triangulare (Retz.) Schindl. |
|
|
|
|
Derris
heyneana (Wight an&d Arn.) Benth. |
|
Endemic
PI |
|
|
Desmodium
heterocarpon (L.) DC. |
|
|
|
|
Desmodium
laxiflorum DC. |
|
|
|
|
Desmodium
motorium (Houtt.) Merr. |
|
|
|
|
Desmodium
triflorum (L.) DC. |
|
|
|
|
Erithrina
stricta Roxb. |
Pangaro |
|
|
|
Flemingia
macrophylla (Willd.) Kuntze ex Merr. |
|
|
|
|
Flemingia
strobilifera (L.) R.Br. ex W.T.Aiton |
|
|
|
|
Flemingia
tuberosa Dalzell |
|
Endemic
PI |
|
|
Geissaspis
cristata Wight & Arn. |
|
|
|
|
Geissaspis
tenella Benth. |
|
Endemic
PI |
|
|
Indigofera
dalzelli T.Cooke |
|
Endemic
WG |
|
|
Indigofera
prostrata Willd. |
|
Endemic
PI |
|
|
Mucuna
monosperma DC. |
|
|
|
|
Paraderris
canarensis (Dalzell) Adema |
|
|
|
|
Pongamia
pinnata (L.) Pierre |
Karanji |
|
|
|
Sesbania
bispinosa (Jacq.) W.Wight |
|
|
|
|
Smithia
bigemina Dalzell |
|
|
|
|
Smithia
conferta J.E.Sm |
|
|
|
|
Smithia
salsuginea Hance |
|
Endemic
PI |
|
|
Spatholobus
parviflorus (Roxb. ex DC.) Kuntze |
|
|
|
|
Spatholobus
purpureus Benth. ex Prain |
|
|
|
|
Tadehagi
triquetrum (L.) H.Ohashi |
|
|
|
|
Tephrosia
candida (Roxb.) DC. |
|
|
|
|
Tephrosia
coccinea Wall. |
|
Endemic
PI |
|
|
Teramnus
labialis (L.f.) Spreng. |
|
|
|
|
Uraria
rufescens (DC) Schindl. |
|
|
|
|
Vigna
vexillata (L.) A.Rich. |
|
|
|
|
LENTIBULARIACEAE |
|
|
|
|
Utricularia
caerulea L. |
|
|
|
|
Utricularia
graminifolia Vahl |
|
|
|
|
Utricularia
lazulina P.Taylor |
|
|
|
|
Utricularia
purpurascens J.Graham |
|
|
|
|
Utricularia
reticulata Sm. |
|
|
|
|
Utricularia
striatula Sm. |
|
|
|
|
Utricularia
uliginosa Vahl. |
|
|
|
|
LOGANIACEAE |
|
|
|
|
Strychnos
nux-vomica L. |
Kajro |
|
|
|
Strychnos
minor Dennst. |
|
|
|
|
LORANTHACEAE |
|
|
|
|
Dendrophthoe
falcata (L.f.) Blume |
|
|
|
|
Elytranthe
capitellata (Wight & Arn.) Engl. |
|
|
|
|
Scurrula
parasitica L. |
|
|
|
|
Taxillus
tomentosus (B.Heyne ex W.Roth) Tiegh. |
|
|
|
|
Tolypanthus
lagenifer (Wight) Tiegh. |
|
Endemic
WG |
|
|
LYTHRACEAE |
|
|
|
|
Lagerstroemia
microcarpa Wight |
Nana |
|
|
|
Lagerstroemia
parviflora Roxb. |
|
|
|
|
Rotala
densiflora (Roth ex Roem. & Schult.)
Koehne |
|
|
|
|
Rotala
rotundifolia (Buch.-Ham. ex Roxb.) Koehne |
|
|
|
|
Woodfordia
fruticosa (L.) Kurz |
Dhayti |
|
|
|
MALPIGHIACEAE |
|
|
|
|
Aspidopterys
canarensis Dalzell |
|
Endemic
WG |
CR |
|
MALVACEAE |
|
|
|
|
Abelmoschus
manihot (L.) Medik. |
Ambadi |
|
|
|
Abutilon
persicum (Burm.f.) Merr. |
|
|
|
|
Daceschistia
trilobata Wight |
|
Endemic
WG |
|
|
Hibiscus
hirtus L. |
|
|
|
|
Hibiscus
hispidissimus Griff. |
|
|
|
|
Kydia
calycina Roxb. |
|
|
|
|
Sida
acuta Burm.f. |
|
|
|
|
Sida
cordata (Burm.f.) Borss. |
|
|
|
|
Sida
rhombifolia L. |
Tupkadi |
|
|
|
Thespesia
lampas (Cav.) Dalzell ex Dalzell &
A.Gibson |
|
|
|
|
Urena
lobata L. |
|
|
|
|
MARANTACEAE |
|
|
|
|
Schumannianthus
virgatus (Roxb.) Rolfe |
|
|
|
|
MELASTOMATACEAE |
|
|
|
|
Melastoma
malabathiricum L. |
|
|
|
|
Memecylon
talbotianum D.Brandis |
|
|
|
|
Memecylon
terminale Dalzell |
|
Endemic PI |
|
|
Memecylon
umbellatum Burm.f. |
|
|
|
|
Memecylon
wightii Thwaites |
|
|
|
|
Osbeckia
muralis Naud. |
|
|
|
|
MELIACEAE |
|
|
|
|
Aglaia
eleagnoidea (A.Juss.) Benth. |
|
|
|
|
Aglaia
lawii (Wight) C.J. Saldanha ex Ramamoorthy |
Maharsangal |
|
|
|
Chukrasia
tabularis A.Juss. |
|
Endemic IND |
|
|
Naregamia
alata Wight & Arn. |
Pitmado |
Endemic IND |
|
|
Toona
ciliata M.Roem. |
|
|
|
|
Trichlia
connaroides (Wigh & Arn.) Bentv. |
|
|
|
|
Turraea
villosa A.W.Benn. |
|
|
|
|
Walsura
trifoliata (A.Juss.) Harms |
|
|
|
|
MENISPERMACEAE |
|
|
|
|
Anamirta
cocculus (L.) Wight & Arn. |
|
|
|
|
Cocculus
hirsutus (L.) Theob. |
|
|
|
|
Cyclea
peltata (Lam.) Hook.f. & Thomson |
|
|
|
|
Diploclisia
glaucescens (Blume) Diels |
Ramwel, Ramrukhi |
|
|
|
Stephania
elegans Hook. f. & Thomson |
|
|
|
|
Stephania
japonica (Thunb.) Miers |
|
|
|
|
MOLLUGINACEAE |
|
|
|
|
Glinus
oppositifolius (L.) A.DC. |
|
|
|
|
MORACEAE |
|
|
|
|
Artocarpus
gomezianus Wall. ex Trecul ssp. zeylanicus
Jarrett |
Patphanas |
|
|
|
Artocarpus
heterophyllus Lam. |
Patphanas |
Endemic WG |
|
|
Artocarpus
hirsutus Lam. |
Patphanas |
|
|
|
Ficus
arnottiana (Miq.) Miq. |
Payar |
|
|
|
Ficus
benghalensis L. |
Wad |
|
|
|
Ficus
callosa Willd. |
|
|
|
|
Ficus
drupacea Thunb. var. pubescens (Roth)
Corner |
|
|
|
|
Ficus
exasperata Vahl |
|
|
|
|
Ficus
heterophylla L.f. |
|
|
|
|
Ficus
hispida L.f. |
Karwat |
|
|
|
Ficus
microcarpa L.f. |
Nandangol |
|
|
|
Ficus
nervosa Heyne ex Roth |
|
|
|
|
Ficus
racemosa L. |
Rumad |
|
|
|
Ficus
tinctoria G.Forst. ssp. parasitica (Koenig
ex Willd.) Corner |
|
|
|
|
Ficus
tsjahela Burm.f. |
Kel |
|
|
|
MUSACEAE |
|
|
|
|
Ensete
superbum (Roxb.) Cheesman |
|
Endemic WG |
|
|
Musa
x paradisiaca L. |
Keli |
|
|
|
MYRISTICACEAE |
|
|
|
|
Knema
attenuata (Wall. ex Hook.f. &
Thomson) Warb. |
|
Endemic WG |
|
|
Myristica
malabarica Lam. |
|
Endemic WG |
|
|
MYRSINACEAE |
|
|
|
|
Ardisia
solanacea Roxb. |
Bugadi |
|
|
|
Embelia
tsjeriam-cottam (Roem. & Schult.) DC. |
|
|
|
|
Maesa
indica (Roxb.) DC. |
|
|
|
|
MYRTACEAE |
|
|
|
|
Eugenia
mooniana Wight |
|
|
|
|
Eugenia
roxburghii DC. |
|
|
|
|
Syzygium
caryophyllatum (L.) Alston |
Bhirand |
|
|
|
Syzygium
cumini (L.) Skeels |
Bhirand |
|
|
|
Syzygium
hemisphericum (Wight) Alston |
Zamlo |
|
|
|
Syzygium
laetum (Buch.-Ham.) Gandhi |
|
Endemic
SWI |
|
|
Syzygium
salicifolium (Wight) J.Graham |
|
Endemic
SWI |
|
|
Syzygium
zeylanicum (L.) DC. |
|
|
|
|
OCHNACEAE |
|
|
|
|
Ochna
obtusata DC. |
|
|
|
|
OLACACEAE |
|
|
|
|
Olax
imbricata Roxb. |
|
|
|
|
OLEACEAE |
|
|
|
|
Jasminum
coarctatum Roxb. |
|
|
|
|
Jasminum
malabaricum Wight |
|
Endemic
PI |
|
|
Jasminum
multiflorum (Burm.f.) Andr. |
|
|
|
|
Jasminum
ritchiei C.B.Clarke |
|
|
|
|
Ligustrum
perrottetii A.DC. |
|
Endemic
WG |
|
|
Olea
dioica Roxb. |
|
|
|
|
Schrebera
swietenoides Roxb. |
|
|
|
|
ONAGRACEAE |
|
|
|
|
Ludwigia
hyssopifolia (G.Don) Exell |
|
|
|
|
Ludwigia
octovalvis (Jacq.) P.H.Raven ssp. octovalvis |
|
|
|
|
Ludwigia
octovalvis (Jacq.) P.H.Raven ssp. sessiliflora (Micheli)
P.H.Raven |
|
|
|
|
ORCHIDACEAE |
|
|
|
|
Acampe
praemorsa (Roxb.) Blatt. & McCann |
|
|
|
|
Aerides
crispa Lindl. |
|
Endemic
WG |
|
|
Aerides
maculosa Lindl. |
|
Endemic
PI |
|
|
Aerides
ringens (Lindl.) C.E.C.Fisch. |
|
|
|
|
Bulbophyllum
neilgherrense Wight |
Bendli |
Endemic
WG |
|
|
Cleisostoma
tenuifolium (L.) Garay |
|
|
|
|
Conchidium
microchilos (Dalzell) Rauschert |
|
Endemic
PI |
|
|
Cottonia
peduncularis (Lindl.) Rchb.f. |
|
|
|
|
Cymbidium
aloifolium (L.) Sw. |
|
|
|
|
Dendrobium
barbatulum Lindl. |
|
Endemic
WG |
|
|
Gastrochilus
flabelliformis (Blatt. & McCann) C.J.Saldanha |
|
Endemic
WG |
|
|
Habenaria
diphylla (Nimmo) Dalzell |
|
|
|
|
Habenaria
heyneana Lindl. |
|
Endemic
PI |
|
|
Habenaria
longicorniculata J.Graham |
|
Endemic
PI |
|
|
Habenaria
marginata Coleb. |
|
|
|
|
Habenaria
multicaudata Sedgew. |
|
Endemic
WG |
EN |
|
Habenaria
plantaginea Lindl. |
|
|
|
|
Liparis
deflexa Hook.f. |
|
|
|
|
Liparis
nervosa (Thunb.) Lindl. |
|
|
|
|
Luisia
tenuifolia Blume |
|
Endemic
WG |
|
|
Malaxis
versicolor (Lindl.) Abeyw. |
|
|
|
|
Nervilia
aragoana Gaudich. |
|
|
|
|
Oberonia
brachyphylla Blatt. & McCann |
|
Endemic
WG |
VU |
|
Pecteilis
gigantea (J.E.Sm.) Raf. |
|
|
|
|
Peristylus
plantagineus (Lindl.) Lindl. |
|
|
|
|
Pholidota
imbricata Hook. |
|
|
|
|
Porpax
jerdoniana (Wight) Rolfe |
|
Endemic
WG |
|
|
Porpax
reticulata Lindl. |
|
|
|
|
Rhynchostylis
retusa (L.) Blume |
|
|
|
|
Smithsonia
viridiflora (Dalzell) C.J.Saldhanha |
|
|
|
|
Tropidia
angulosa (Lindl.) Blume |
|
|
|
|
Vanda
tessellata (Roxb.) Hook. ex G.Don |
|
|
|
|
Vanda
testacea (Lindl.) Rchb. |
|
|
|
|
Zeuxine
longilabris (Lindl) Trim |
|
|
|
|
OROBANCHACEAE |
|
|
|
|
Aeginetia
indica L. |
|
|
|
|
OXALIDACEAE |
|
|
|
|
Biophytum
sensitivum (L.) DC. |
|
|
|
|
Oxalis
corniculata L. |
|
|
|
|
PANDANACEAE |
|
|
|
|
Pandanus
odorifer (Forssk.) Kuntze |
|
|
|
|
PAPAVERACEAE |
|
|
|
|
Argemone
mexicana L. |
|
|
|
|
PASSIFLORACEAE |
|
|
|
|
Adenia
hondala (Gaertn.) J.Wilde |
Salkando |
|
|
|
PEDALIACEAE |
|
|
|
|
Sesamum
orientale L. |
|
|
|
|
PIPERACEACE |
|
|
|
|
Peperomia
pellucida (L.) Humb. |
|
|
|
|
Piper
argyrophyllum Miq. |
Miri |
|
|
|
Piper
nigrum L. |
|
|
|
|
PITTOSPORACEAE |
|
|
|
|
Pittosporum
dasycaulon Miq. |
|
Endemic
WG |
|
|
POACEAE |
|
|
|
|
Apluda
mutica L. |
|
|
|
|
Arundinella
leptochloa (Nees ex Steud.) Hook.f. |
|
Endemic
PI |
|
|
Arundinella
metzii Hocht ex Micq. |
|
Endemic
PI |
|
|
Arundinella
pumila (Hochst. ex A.Rich.) Steud. |
|
|
|
|
Bambusa
bambos (L.) Voss |
|
|
|
|
Brachiaria
ramosa (L.) Stapf |
|
|
|
|
Capillipedium
filiculme (Hook.f.) Stapf |
|
Endemic
PI |
|
|
Centotheca
lappacea (L.) Desv. |
|
|
|
|
Cynodon
dactylon (L.) Pers. |
|
|
|
|
Cyrtococcum
oxyphyllum (Hochst. ex Steud.) Stapf |
|
|
|
|
Dendrocalamus
strictus (Roxb.) Nees |
|
|
|
|
Dichanthium
annulatum (Forssk.) Stapf |
|
|
|
|
Dimeria
stapfiana C.E.Hubb. ex Pilger |
|
|
|
|
Echinochloa
colona (L.) Link |
|
|
|
|
Eragrostis
gangetica (Roxb.) Steud. |
|
|
|
|
Eragrostis
unioloides (Retz.) Nees ex Steud. |
|
|
|
|
Eulalia
trispicata (Schult.) Henrard |
|
|
|
|
Garnotia
arborum Stapf. ex T.Cooke |
|
Endemic
PI |
|
|
Glyphochloa
acuminata (Hack.) Clayton |
|
Endemic
WG |
|
|
Glyphochloa
veldkampii M.A.Fonseca & Janarth. |
|
Endemic
Goa |
CR |
|
Isachne
globosa (Thunb.) Kuntze |
|
|
|
|
Ischaemum
barbatum Retz. |
|
|
|
|
Ischaemum
dalzellii Stapf. ex Bor |
|
|
|
|
Ischaemum
semisagittatum Roxb. |
|
|
|
|
Jansenella
griffithiana (C.Muell.) Bor |
|
|
|
|
Ochlandra
talboti Brandis |
|
|
|
|
Oplismenus
burmanni (Retz.) P.Beauv. |
|
|
|
|
Oplismenus
compositus (L.) P.Beauv. |
|
|
|
|
Panicum
antidotle Retz. |
|
|
|
|
Paspalum
canarae (Steud.) Veldk. |
|
|
|
|
Paspalum
scrobiculatum L. |
|
|
|
|
Pennisetum
pedicellatum Trin. |
|
|
|
|
Pennisetum
polystachion (L.) Schult. |
|
|
|
|
Polytrias
indica (Houtt.) Veldkamp |
|
|
|
|
Pseudanthistiria
heteroclita (Roxb.) Hook.f. |
|
|
|
|
Pseudoxytenanthera
stocksii (Munro) T.Q.Nguyen |
|
|
|
|
Sacciolepis
indica (L.) A.Chase |
|
|
|
|
Setaria
pumila (Poir.) Roem. & Schult. |
|
|
|
|
Spodiopogon
rhizophorus (Steud.) Pilger |
|
|
|
|
Themeda
triandra Forssk. |
|
|
|
|
PODOSTEMACEAE |
|
|
|
|
Dalzellia
ceylanica (Gardn.) Wight |
|
|
|
|
Zeylanidium
sessile (Willis) C.D.K.Cook & Rutish. |
|
|
|
|
POLYGALACEAE |
|
|
|
|
Polygala
elongata Klein ex Willd. |
|
Endemic
IND |
|
|
Salmonia
ciliata (L.) DC. |
|
|
|
|
POLYGONACEAE |
|
|
|
|
Persicaria
glabra (Willd.) M.Gomez |
|
|
|
|
Persicaria
auriculata (Meissn.) S.K.Dixit, B.Datt &
G.P.Roy |
|
|
|
|
Polygonum
plebeium R.Br. |
|
|
|
|
PONTEDERIACEAE |
|
|
|
|
Monochoria
vaginalis (Burm.f.) C.Presl |
|
|
|
|
PORTULACACEAE |
|
|
|
|
Portulaca
oleracea L. |
Gungune |
|
|
|
RANUNCULACEAE |
|
|
|
|
Clematis
gauriana Roxb. ex DC. |
|
|
|
|
Naravelia
zeylanica (L.) DC. |
|
|
|
|
RHIZOPHORACEAE |
|
|
|
|
Carallia
brachiata (Lour.) Merr. |
Phanshi |
|
|
|
RHAMNACEAE |
|
|
|
|
Gauania
microcarpa DC. |
|
|
|
|
Scutia
myrtina (Burm.f.) Kurz. |
|
|
|
|
Smythea
bombaiensis (Dalzell) S.P.Banerjee & P.K.Mukh. |
|
Endemic
WG |
|
|
Ventilago
denticulata Willd. |
|
Endemic
IND |
|
|
Ziziphus
mauritiana Lam. |
|
|
|
|
Ziziphus
oenoplia (L.) Mill. |
|
|
|
|
Ziziphus
rugosa Lam. |
Churan |
|
|
|
Ziziphus
xylopyra (Retz.) Willd. |
|
|
|
|
RUBIACEAE |
|
|
|
|
Argostemma
courtallense Arn. |
|
Endemic
WG |
|
|
Argostemma
verticillatum Wall. |
|
|
|
|
Canthium
rheedei DC. |
|
|
|
|
Catunaregam
spinosa (Thunb.) Tirveng. |
Gela |
|
|
|
Chassalia
curviflora (Wall.) Thwaites var. ophioxyloides (Wall.)
Deb & B.Krishna |
|
|
|
|
Discospermum
sphaerocarpum Dalzell ex Hook.f. |
|
|
EN |
|
Haldina
cordifolia (Roxb.) Ridsdale |
Hedu |
|
|
|
Hedyotis
auricularia L. |
|
|
|
|
Hedyotis
corymbosa (L.) Lam. |
|
|
|
|
Hedyotis
herbacea L. |
|
|
|
|
Hedyotis
trinervia (Retz.) Roem. & Schult. |
|
|
|
|
Hymenodictyon
obovatum Wall. |
|
Endemic
IND |
|
|
Ixora
brachiata Roxb. |
|
Endemic
IND |
|
|
Ixora
coccinia L. |
Pentkul |
|
|
|
Ixora
elongata B.Heyne ex G.Don |
|
|
|
|
Ixora
malabarica (Dennst.) Mabb. |
|
|
|
|
Ixora
nigricans R. Br. Wight & Arn. |
|
|
|
|
Meyna
laxiflora Robyns |
|
|
|
|
Mitragyna
parvifolia (Roxb.) Korth. |
|
|
|
|
Mussaenda
glabrata (Hook.f. ) Hutch. ex Gamble |
Sharwad |
Endemic
PI |
|
|
Mussaenda
laxa (Hook.f.) Hutch. ex Gamble |
Sharwad |
Endemic
WI |
|
|
Neanotis
rheedei (Wall. ex Wight & Arn.)
W.H.Lewis |
|
Endemic
WG |
|
|
Neanotis
subtilis (Miq.) Govaerts |
|
Endemic
WG |
|
|
Neolamarckia
cadamba (Roxb.) Bosser |
Kadamb |
|
|
|
Neonauclea
purpurea (Roxb.) Merr. |
|
|
|
|
Ophiorrhiza
rugosa Wall. var. prostrata (D. Don) Deb
& D.C.Mondal |
|
|
|
|
Oxyceros
rugulosus (Thw) Tirveng. |
|
|
|
|
Pavetta
crassicaulis Bremek. |
|
|
|
|
Pavetta
indica L. var. tomentosa (Roxb. ex Sm.)
Hook.f. |
|
|
|
|
Psychotria
dalzellii Hook.f. |
Endi |
Endemic
WG |
|
|
Psydrax
umbellata (Wight) Bridson |
Tupya |
|
|
|
Rubia
cordifolia L. |
|
|
|
|
Saprosma
glomeratum (Gardn.) Bedd. |
|
Endemic
PI |
|
|
Spermacoce
articularis L. |
|
|
|
|
Spermacoce
ocymoides Burm.f. |
|
|
|
|
Spermacoce
pusilla Wall. |
|
|
|
|
Tamilnadia
uliginosa (Retz.) Tirveng. & Sastre |
|
|
|
|
Wendlandia
thyrsoidea (Roth) Steud. |
|
Endemic
WG |
|
|
RUTACEAE |
|
|
|
|
Atlantia
racemosa Wight |
Malkadlimbi |
|
|
|
Atlantia
wightii Tanaka |
|
Endemic
WG |
|
|
Glycosmis
pentaphylla (Retz.) DC. |
Menaka |
|
|
|
Luvunga
eleutherandra Dalzell |
|
Endemic
WG |
|
|
Milicope
lunu-ankenda (Gaertn.) T.G.Hartely |
|
|
|
|
Murraya
koenigii (L.) Spreng. |
Karpil |
|
|
|
Murraya
paniculata Jack |
|
|
|
|
Paramigna
monophylla Wight |
|
|
|
|
Toddalia
asiatica (L.) Lam. |
|
|
|
|
Zanthoxylum
rhetsa (Roxb.) DC. |
Tirphal |
|
|
|
SANTALACEAE |
|
|
|
|
Osyris
quadripartita Salzm. ex Decne. |
|
|
|
|
SAPINDACEAE
|
|
|
|
|
Allophylus
cobbe (L.) Raeusch. |
|
|
|
|
Dimocarus
longan Lour. |
|
|
|
|
Harpullia
arborea (Blanco) Radlk. |
|
|
|
|
Lepisanthus
tetraphylla (Vahl) Radlk. |
|
|
|
|
Schleichera
oleosa (Lour.) Oken |
Koshim |
|
|
|
SAPOTACEAE |
|
|
|
|
Chrysophyllum
roxburghii G.Don |
|
|
|
|
Mimusops
elengi L. |
Owal |
|
|
|
Palaquium
ellipticum (Dalzell) Baill. |
|
|
|
|
Xantolis
tomentosa (Roxb.) Raf. |
Kumbal |
|
|
|
SCROPHULARIACEAE |
|
|
|
|
Angelonia
gardneri Hook. |
|
|
|
|
Centranthera
indica (L.) Gamble |
|
|
|
|
Dopatrium
junceum (Roxb.) Buch.-Ham. ex Benth. |
|
|
|
|
Lindernia
antipoda (L.) Alston. |
|
|
|
|
Lindernia
caespitosa (Blume) Panigrahi |
|
|
|
|
Lindernia
ciliata (Colsm.) Pennell |
|
|
|
|
Lindernia
crustacea (L.) F. Muell. |
|
|
|
|
Lindernia
multiflora (Roxb.) Mukerjee |
|
|
|
|
Lindernia
oppositifolia (Retz.) Mukerjee |
|
|
|
|
Mecardonia
procumbens (Mill.) Small |
|
|
|
|
Rhamphicarpa
longiflora (Arn.) Benth. |
|
Endemic
WG |
|
|
Scoparia
dulcis L. |
|
|
|
|
Striga
asiatica (L.) Kuntze |
|
|
|
|
Striga
gesnerioides (Willd.) Vatke ex Engl. |
|
|
|
|
Torenia
indica C.J.Saldanha |
|
Endemic
WG |
|
|
Torenia
violacea (Azaolo ex Blanco) Pennell |
|
|
|
|
SMILACACEAE |
|
|
|
|
Smilax
zeylanica L. |
|
|
|
|
SOLANACEAE |
|
|
|
|
Lycianthes
laevis (Dunal) Bitter |
|
|
|
|
Physalis
minima L. |
|
|
|
|
Solanum
anguivi Lam. |
|
|
|
|
STERCULIACEAE |
|
|
|
|
Helicteres
isora L. |
Kewan |
|
|
|
Melochia
corchorifolia L. |
|
|
|
|
Pterospermum
diversifolium Blume |
Mothi Daman |
|
|
|
Sterculia
guttata Roxb. ex DC. |
|
|
|
|
SYMPLOCACEAE |
|
|
|
|
Symplocos
cochinchinensis (Lour.) S. Moore ssp. laurina
(Retz.) Noot. |
|
|
|
|
Symplocos
racemosa Roxb. |
|
|
|
|
THYMELAEACEAE |
|
|
|
|
Gnidia
glauca (Fresen.) Gilg. |
|
|
|
|
TILIACEAE |
|
|
|
|
Corchorus
capsularis L. |
|
|
|
|
Corchorus
olitorius L. |
|
|
|
|
Grewia
nervosa (Lour.) Panigrahi |
Asoli, Chiwar |
|
|
|
Grewia
serrulata DC. |
Chopdi |
|
|
|
Grewia
tillifolia Vahl |
Dhaman |
|
|
|
Triumfetta
rhomboidea Jacq. |
|
|
|
|
ULMACEAE |
|
|
|
|
Celtis
timorensis Spanoghe |
|
|
|
|
Holoptelea
integrifolia (Roxb.) Planch. |
Wawal |
|
|
|
Trema
orientalis (L.) Blume |
|
|
|
|
URTICACEAE |
|
|
|
|
Boehmeria
macrophylla Hornem. |
|
|
|
|
Debregeasia
longifolia (Burm.f.) Wedd. |
|
|
|
|
Laportea
interrupta (L.) Chew |
|
|
|
|
Pilea
microphylla (L.) Liebm. |
|
|
|
|
VERBENACEAE |
|
|
|
|
Lantana
camara L. |
|
|
|
|
VISCACEAE |
|
|
|
|
Viscum
monoicum Roxb. ex DC. |
|
|
|
|
VITACEAE |
|
|
|
|
Ampelocissus
indica (L.) Planch. |
|
|
|
|
Amplelocissus
latifolia (Roxb.) Planch. |
|
|
|
|
Caryatia
tenuifolia (Wight and Arn.) Gagnep. |
|
|
|
|
Caryatia
trifolia (L.) Domin |
|
|
|
|
Cissus
elongata Roxb. |
|
|
|
|
Cissus
javanica DC. |
|
|
|
|
Cissus
rependa Vahl |
Palkonde |
|
|
|
Cyphostemma
auriculatum (Roxb.) P.Singh & B.V.Shetty |
|
|
|
|
Tetrastigma
sulcatum (M.A.Lawson) Gamble |
|
|
|
|
ZINGIBERACEAE |
|
|
|
|
Alpinia
galanga (L.) Willd. |
|
|
|
|
Curcuma
decipiens Dalzell |
|
Endemic
PI |
|
|
Curcuma
zanthorrhiza Roxb. |
|
|
|
|
Kaempferia
scaposa (Nimmo) Benth. |
|
Endemic
WG |
|
|
Zingiber
neesanum (J. Graham) Ramamoorthy |
|
Endemic
PI |
|
|
Zingiber
nimmonii (J. Graham) Dalzell |
|
Endemic
PI |
|
|
Zingiber
zerumbet (L.) Roscoe ex J.E.Sm. |
|
|
|
Appendix
III. Checklist of mammal species in Bhagwan Mahavir Sanctuary derived from
open-source lists, IUCN Red List database and field-guides on Indian mammals
|
|
Order |
Family |
Species |
Common
name |
IUCN
Red List Category$ |
WPA
schedule$ |
|
1 |
Carnivora |
Felidae |
Panthera
tigris |
Bengal Tiger |
Endangered |
I |
|
2 |
Carnivora |
Felidae |
Panthera
pardus |
Common Leopard |
Vulnerable |
I |
|
3 |
Carnivora |
Felidae |
Prionailurus
bengalensis |
Leopard Cat |
Least Concern |
I |
|
4 |
Carnivora |
Felidae |
Prionailurus
rubiginosus |
Rusty-spotted Cat |
Near Threatened |
I |
|
5 |
Carnivora |
Felidae |
Felis
chaus |
Jungle Cat |
Least Concern |
II |
|
6 |
Carnivora |
Canidae |
Cuon
alpinus |
Dhole |
Endangered |
II |
|
7 |
Carnivora |
Canidae |
Canis
aureus |
Golden Jackal |
Least Concern |
II |
|
8 |
Carnivora |
Ursidae |
Melursus
ursinus |
Sloth Bear |
Vulnerable |
I |
|
9 |
Carnivora |
Herpestidae |
Herpestes/
Urva vitticollis |
Stripe-necked Mongoose |
Least Concern |
II |
|
10 |
Carnivora |
Herpestidae |
Herpestes/
Urva smithii |
Ruddy Mongoose |
Least Concern |
II |
|
11 |
Carnivora |
Herpestidae |
Urva
edwardsii |
Indian Grey Mongoose |
Least Concern |
II |
|
12 |
Carnivora |
Mustelidae |
Aonyx
cinereus |
Small-clawed Otter |
Vulnerable |
I |
|
13 |
Carnivora |
Mustelidae |
Lutrogale
perspicillata |
Smooth-coated Otter |
Vulnerable |
II |
|
14 |
Carnivora |
Viverridae |
Viverricula
indica |
Small Indian Civet |
Least Concern |
II |
|
15 |
Carnivora |
Viverridae |
Paradoxurus
jerdoni |
Brown Palm Civet |
Least Concern |
II |
|
16 |
Carnivora |
Viverridae |
Paradoxurus
hermaphroditus |
Common Palm Civet |
Least Concern |
II |
|
17 |
Cetartiodactyla |
Bovidae |
Bos
gaurus |
Gaur |
Vulnerable |
I |
|
18 |
Cetartiodactyla |
Bovidae |
Tetracerus
quadricornis |
Four-horned antelope |
Vulnerable |
I |
|
19 |
Cetartiodactyla |
Cervidae |
Rusa
unicolor |
Sambar |
Vulnerable |
III |
|
20 |
Cetartiodactyla |
Cervidae |
Axis
axis |
Chital |
Least Concern |
III |
|
21 |
Cetartiodactyla |
Cervidae |
Muntiacus
vaginalis |
Northern Red Muntjac |
Least Concern |
III |
|
22 |
Cetartiodactyla |
Tragulidae |
Moschiola
indica |
Indian Chevrotain/ Mouse deer |
Least Concern |
I |
|
23 |
Cetartiodactyla |
Suidae |
Sus
scrofa |
Wild Boar |
Least Concern |
III |
|
24 |
Pholidota |
Manidae |
Manis
crassicaudata |
Indian Pangolin |
Endangered |
I |
|
25 |
Primates |
Cercopithecidae |
Semnopithecus
hypoleucos |
Black-footed Gray Langur |
Vulnerable |
II |
|
26 |
Primates |
Cercopithecidae |
Macaca
radiata |
Bonnet Macaque |
Least Concern |
II |
|
27 |
Primates |
Lorisidae |
Loris
lydekkerianus |
Slender Loris |
Least Concern |
I |
|
28 |
Lagomorpha |
Leporidae |
Lepus
nigricollis |
Indian Hare |
Least Concern |
IV |
|
29 |
Rodentia |
Sciuridae |
Ratufa
indica |
Indian Giant Squirrel |
Least Concern |
II |
|
30 |
Rodentia |
Sciuridae |
Petaurista
philippensis |
Indian Giant Gliding Squirrel |
Least Concern |
II |
|
31 |
Rodentia |
Sciuridae |
Funambulus
tristriatus |
Western Ghats Striped Squirrel |
Least Concern |
IVa |
|
32 |
Rodentia |
Sciuridae |
Funambulus
palmarum |
Common Palm Squirrel |
Least Concern |
IVa |
|
33 |
Rodentia |
Hystricidae |
Hystrix
indica |
Indian Crested Porcupine |
Least Concern |
IV |
|
34 |
Rodentia |
Muridae |
Tatera
indica |
Indian Gerbil |
Least Concern |
Vb |
|
35 |
Rodentia |
Muridae |
Vandeleuria
oleracea |
Asiatic Long-tailed Climbing
Mouse |
Least Concern |
Vb |
|
36 |
Rodentia |
Muridae |
Mus
musculus |
House Mouse |
Least Concern |
Vb |
|
37 |
Rodentia |
Muridae |
Mus
booduga |
Indian Field Mouse |
Least Concern |
Vb |
|
38 |
Rodentia |
Muridae |
Mus
saxicola |
Brown Spiny Mouse |
Least Concern |
Vb |
|
39 |
Rodentia |
Muridae |
Mus
terricolor* |
Pygmy Field Mouse |
Least Concern |
Vb |
|
40 |
Rodentia |
Muridae |
Millardia
meltada* |
Soft-furred Metad |
Least Concern |
Vb |
|
41 |
Rodentia |
Muridae |
Madromys
blanfordi |
White-tailed Wood Rat |
Least Concern |
Vb |
|
42 |
Rodentia |
Muridae |
Golunda
ellioti |
Indian Bush-rat |
Least Concern |
Vb |
|
43 |
Rodentia |
Muridae |
Bandicota
indica |
Greater Bandicoot Rat |
Least Concern |
Vb |
|
44 |
Rodentia |
Muridae |
Bandicota
bengalensis |
Lesser Bandicoot Rat |
Least Concern |
Vb |
|
45 |
Rodentia |
Muridae |
Rattus
rattus |
House Rat |
Least Concern |
Vb |
|
46 |
Rodentia |
Muridae |
Rattus
satarae* |
Sahyadris Forest Rat |
Vulnerable |
Vb |
|
47 |
Chiroptera |
Pteropodidae |
Pteropus medius |
Indian Flying Fox Bat |
Least Concern |
Vb |
|
48 |
Chiroptera |
Pteropodidae |
Rousettus
leschenaultii |
Leschenault’s Rousette |
Least Concern |
Vb |
|
49 |
Chiroptera |
Pteropodidae |
Cynopterus
sphinx |
Greater Short-nosed Fruit Bat |
Least Concern |
Vb |
|
50 |
Chiroptera |
Pteropodidae |
Cynopterus
brachyotis |
Lesser Short-nosed Fruit Bat |
Least Concern |
Vb |
|
51 |
Chiroptera |
Pteropodidae |
Eonycteris
spelaea* |
Dawn Bat |
Least Concern |
Vb |
|
52 |
Chiroptera |
Molossidae |
Tadarida
aegyptiaca* |
Egyptian Free-tailed Bat |
Least Concern |
|
|
53 |
Chiroptera |
Molossidae |
Chaerephon
plicatus* |
Wrinkle-lipped Free-tailed Bat |
Least Concern |
|
|
54 |
Chiroptera |
Molossidae |
Otomops wroughtoni* |
Wroughton’s Free-tailed Bat |
Data Deficient |
I |
|
55 |
Chiroptera |
Emballonuridae |
Taphozous
longimanus* |
Long-winged Tomb Bat |
Least Concern |
|
|
56 |
Chiroptera |
Emballonuridae |
Taphozous
nudiventris* |
Naked-rumped Tomb Bat |
Least Concern |
|
|
57 |
Chiroptera |
Emballonuridae |
Taphozous
melanopogon |
Black-bearded Tomb Bat |
Least Concern |
|
|
58 |
Chiroptera |
Emballonuridae |
Taphozous
theobaldi* |
Theobold’s Bat |
Least Concern |
|
|
59 |
Chiroptera |
Emballonuridae |
Saccolaimus
saccolaimus* |
Bare-rumped Sheathtail Bat |
Least Concern |
|
|
60 |
Chiroptera |
Megadermatidae |
Megaderma
lyra* |
Greater False Vampire Bat |
Least Concern |
|
|
61 |
Chiroptera |
Megadermatidae |
Megaderma
spasma |
Lesser False Vampire Bat |
Least Concern |
|
|
62 |
Chiroptera |
Rhinolophidae |
Rhinolophus
rouxii |
Rufous Horseshoe Bat |
Least Concern |
|
|
63 |
Chiroptera |
Rhinolophidae |
Rhinolophus
lepidus |
Blyth’s Horseshoe Bat |
Least Concern |
|
|
64 |
Chiroptera |
Rhinolophidae |
Rhinolophus
beddomei |
Beddome’s Horseshoe Bat |
Least Concern |
|
|
65 |
Chiroptera |
Hipposideridae |
Hipposideros
fulvus* |
Fulvus Leaf-nosed Bat |
Least Concern |
|
|
66 |
Chiroptera |
Hipposideridae |
Hipposideros speoris* |
Schneider’s Leaf-nosed Bat |
Least Concern |
|
|
67 |
Chiroptera |
Hipposideridae |
Hipposideros
galeritus* |
Cantor’s Leaf-nosed Bat |
Least Concern |
|
|
68 |
Chiroptera |
Hipposideridae |
Hipposideros lankadiva |
Kelaart’s Leaf-nosed Bat |
Least Concern |
|
|
69 |
Chiroptera |
Vespertilionidae |
Myotis
horsfieldii* |
Horsfield’s Bat |
Least Concern |
|
|
70 |
Chiroptera |
Vespertilionidae |
Pipistrellus coromandra |
Indian Pipistrelle |
Least Concern |
|
|
71 |
Chiroptera |
Vespertilionidae |
Pipistrellus
tenuis |
Least Pipistrelle |
Least Concern |
|
|
72 |
Chiroptera |
Vespertilionidae |
Pipistrellus
ceylonicus* |
Kelaart’s Pipistrelle |
Least Concern |
|
|
73 |
Chiroptera |
Vespertilionidae |
Scotozous dormeri* |
Dormer’s Bat |
Least Concern |
|
|
74 |
Chiroptera |
Vespertilionidae |
Scotophilus
heathii* |
Greater Asiatic Yellow Bat |
Least Concern |
|
|
75 |
Chiroptera |
Vespertilionidae |
Scotophilus
kuhlii* |
Lesser Asiatic Yellow Bat |
Least Concern |
|
|
76 |
Chiroptera |
Vespertilionidae |
Hesperoptenus
tickelli* |
Tickell’s Bat |
Least Concern |
|
|
77 |
Chiroptera |
Vespertilionidae |
Kerivoula picta |
Painted Bat |
Near Threatened |
|
|
78 |
Chiroptera |
Vespertilionidae |
Tylonycteris
pachypus* |
Lesser Bamboo Bat |
Least Concern |
|
|
79 |
Chiroptera |
Miniopteridae |
Miniopterus
schreibersii ssp. fuliginosus |
Schreiber’s Long-fingered Bat |
Near Threatened |
|
|
80 |
Eulipotyphla |
Soricidae |
Suncus
murinus |
House Shrew |
Least Concern |
|
|
81 |
Scandentia |
Tupaiidae |
Anathana
ellioti |
Madras Tree Shrew |
Least Concern |
|
*Possible occurrence; a Five-striped
palm squirrel mentioned in Schedule IV; bFruit Bats, Mice, &
Rats mentioned in Schedule V; $Distribution records follow
IUCN Range maps and Menon (2014).
Appendix
IV. List of fish species in the Mhadei sub-basin (neighbouring Bhagwan Mahavir
Wildlife Sanctuary), with status in terms of endemicity to the Western Ghats
and IUCN Red List (Atkore 2017).
|
|
Species |
Western
Ghats Endemic |
IUCN
status |
|
1. |
Aplocheilus
lineatus (Valenciennes, 1846) |
|
Least Concern |
|
2. |
Arothron
leopardus (Day, 1878) |
|
Data Deficient |
|
3. |
Carinotetraodon
travancoricus (Hora & Nair, 1941) |
Endemic |
Vulnerable |
|
4. |
Chanda
nama Hamilton, 1822 |
|
Least Concern |
|
5. |
Channa
gachua (Hamilton, 1822) |
|
Least Concern |
|
6. |
Channa
marulius (Hamilton, 1822) |
|
Least Concern |
|
7. |
Channa
striata (Bloch, 1793) |
|
Least Concern |
|
8. |
Dawkinsia
filamentosa (Valenciennes, 1844) |
Endemic |
Least Concern |
|
9. |
Devario
spp |
|
|
|
10. |
Devario
malabaricus (Jerdon, 1849) |
|
Least Concern |
|
11. |
Etroplus
suratensis (Bloch, 1790) |
|
Least Concern |
|
12. |
Garra
bicornuta Narayan Rao, 1920 |
Endemic |
Near Threatened |
|
13. |
Garra
mullya (Sykes, 1839) |
|
Least Concern |
|
14. |
Garra
stenorhynchus (Jerdon, 1849) |
|
Least Concern |
|
15. |
Glossogobius
giuris (Hamilton, 1822) |
|
Least Concern |
|
16. |
Glossogobius
spp. |
|
|
|
17. |
Haludaria
melanampyx (Day, 1865) |
Endemic |
Data Deficient |
|
18. |
Hypselobarbus
curmuca (Hamilton, 1807) |
Endemic |
Endangered |
|
19. |
Hypselobarbus
dobsoni (Day, 1876) |
Endemic |
Data Deficient |
|
20. |
Hypselobarbus
jerdoni (Day, 1870) |
Endemic |
Least Concern |
|
21. |
Lepidocephalichthys
thermalis (Valenciennes 1846) |
|
Least Concern |
|
22. |
Mastacembelus
armatus (Lacépède, 1800) |
|
Least Concern |
|
23. |
Microphis
cuncalus (Hamilton, 1822)* |
|
Least Concern |
|
24. |
Mystus
armatus (Day, 1865) |
|
Least Concern |
|
25. |
Mystus
cavasius (Hamilton, 1822) |
|
Least Concern |
|
26. |
Mystus
gulio (Hamilton, 1822) |
|
Least Concern |
|
27. |
Mystus
keletius (Valenciennes, 1840) |
Endemic |
Least Concern |
|
28. |
Migul
spp. |
|
|
|
29. |
Osteochilichthys
nashii (Day, 1869) |
Endemic |
Least Concern |
|
30. |
Osteochilichthys
thomassi (Day, 1877) |
Endemic |
Least Concern |
|
31. |
Parambassis
ranga (Hamilton, 1822) |
|
Least Concern |
|
32. |
Paracanthocobitis
mooreh (Sykes, 1839) |
Endemic |
|
|
33. |
Pangio
goaensis (Tilak, 1972)* |
Endemic |
Least Concern |
|
34. |
Pethia
narayani (Hora, 1937) |
Endemic |
Least Concern |
|
35. |
Pethia
punctata (Day, 1865) |
Endemic |
Least Concern |
|
36. |
Pethia
setnai (Chhapgar & Sane, 1992) |
Endemic |
Vulnerable |
|
37. |
Pethia
ticto (Hamilton, 1822) |
|
Least Concern |
|
38. |
Pseudetroplus
maculatus (Bloch, 1795) |
|
Least Concern |
|
39. |
Puntius
amphibius (Valenciennes, 1842) |
|
Data Deficient |
|
40. |
Rasbora
daniconius (Hamilton, 1822) |
|
Least Concern |
|
41. |
Rasbora
labiosa Mukerji, 1935 |
Endemic |
Least Concern |
|
42. |
Salmostoma
bacaila (Hamilton, 1822) |
|
Least Concern |
|
43. |
Salmostoma
boopis (Day, 1874) |
|
Least Concern |
|
44. |
Salmostoma
novacula (Valenciennes, 1840) |
|
Least Concern |
|
45. |
Schistura
denisoni (Day, 1867) |
|
Least Concern |
|
46. |
Schistura
spp. |
|
|
|
47. |
Sicyopterus
griseus (Day, 1877) |
Endemic |
Least Concern |
|
48. |
Tor
khudree (Sykes, 1839) |
Endemic |
Least Concern |
|
49. |
Xenentodon
cancila (Hamilton, 1822) |
|
Least Concern |
* Recorded by other researchers in the Mhadei
sub-basin | Pangio goaensis recorded by Talwar & Jhingran
(1991); Microphis cuncalus likely
occurs based on Pollom (2016)
Appendix
V. Checklist of butterfly species in Bhagwan Mahavir Wildlife Sanctuary and
National Park.
|
|
Order |
Family |
Common
name |
Scientific
name |
WPA
Schedule |
|
1 |
Lepidoptera |
Papilionidae |
Southern Birdwing |
Troides
minos |
|
|
2 |
Lepidoptera |
Papilionidae |
Malabar Or Ceylon Rose |
Pachliopta
pandiyana |
|
|
3 |
Lepidoptera |
Papilionidae |
Common Rose |
Pachliopta
aristolochiae |
|
|
4 |
Lepidoptera |
Papilionidae |
Crimson Rose |
Pachliopta
hector |
I |
|
5 |
Lepidoptera |
Papilionidae |
Southern Bluebottle * |
Graphium
teredon |
|
|
6 |
Lepidoptera |
Papilionidae |
Common Jay |
Graphium
doson |
|
|
7 |
Lepidoptera |
Papilionidae |
Tailed Jay |
Graphium
agamemnon |
|
|
8 |
Lepidoptera |
Papilionidae |
Spot Swordtail |
Graphium
nomius |
|
|
9 |
Lepidoptera |
Papilionidae |
Five-Bar Swordtail * |
Graphium
antiphates |
|
|
10 |
Lepidoptera |
Papilionidae |
Common Mime |
Papilio
clytia |
I |
|
11 |
Lepidoptera |
Papilionidae |
Lime |
Papilio
demoleus |
|
|
12 |
Lepidoptera |
Papilionidae |
Malabar Raven |
Papilio
dravidarum |
|
|
13 |
Lepidoptera |
Papilionidae |
Red Helen |
Papilio
helenus |
|
|
14 |
Lepidoptera |
Papilionidae |
Common Mormon |
Papilio
polytes |
|
|
15 |
Lepidoptera |
Papilionidae |
Blue Mormon |
Papilio
polymnestor |
|
|
16 |
Lepidoptera |
Papilionidae |
Paris Peacock |
Papilio
paris |
|
|
17 |
Lepidoptera |
Papilionidae |
Malabar Banded Peacock |
Papilio
budha |
|
|
18 |
Lepidoptera |
Pieridae |
Common Emigrant * |
Catopsilia
pomona |
|
|
19 |
Lepidoptera |
Pieridae |
Mottled Emigrant |
Catopsilia
pyranthe |
|
|
20 |
Lepidoptera |
Pieridae |
Small Grass Yellow |
Eurema
brigitta |
|
|
21 |
Lepidoptera |
Pieridae |
Spotless Grass Yellow |
Eurema
laeta |
|
|
22 |
Lepidoptera |
Pieridae |
Common Grass Yellow |
Eurema
hecabe |
|
|
23 |
Lepidoptera |
Pieridae |
Three-Spot Grass Yellow |
Eurema
blanda |
|
|
24 |
Lepidoptera |
Pieridae |
One-Spot Grass Yellow * |
Eurema
andersonii |
II |
|
25 |
Lepidoptera |
Pieridae |
Common Jezebel |
Delias
eucharis |
|
|
26 |
Lepidoptera |
Pieridae |
Psyche |
Leptosia
nina |
|
|
27 |
Lepidoptera |
Pieridae |
Common Gull |
Cepora
nerissa |
|
|
28 |
Lepidoptera |
Pieridae |
Lesser Gull |
Cepora
nadina |
II |
|
29 |
Lepidoptera |
Pieridae |
Pioneer Or Caper White |
Anaphaeis
aurota |
|
|
30 |
Lepidoptera |
Pieridae |
Plain Puffin * |
Appias
indra |
II |
|
31 |
Lepidoptera |
Pieridae |
Chocolate Albatross * |
Appias
lyncida |
II |
|
32 |
Lepidoptera |
Pieridae |
Common Albatross |
Appias
albina |
II |
|
33 |
Lepidoptera |
Pieridae |
Common Wanderer |
Pareronia
valeria |
II |
|
34 |
Lepidoptera |
Pieridae |
Dark Wanderer |
Pareronia
ceylonica |
|
|
35 |
Lepidoptera |
Pieridae |
Great Orange Tip |
Hebomoia
glaucippe |
|
|
36 |
Lepidoptera |
Nymphalidae |
Southern Duffer * |
Discophora
lepida |
II |
|
37 |
Lepidoptera |
Nymphalidae |
Common Evening Brown |
Melanitis
leda |
|
|
38 |
Lepidoptera |
Nymphalidae |
Great Evening Brown * |
Melanitis
zitenius |
II |
|
39 |
Lepidoptera |
Nymphalidae |
Dark Evening Brown |
Melanitis
phedima |
|
|
40 |
Lepidoptera |
Nymphalidae |
Common Palmfly |
Elymnias
hypermenstra |
|
|
41 |
Lepidoptera |
Nymphalidae |
Bamboo Treebrown * |
Lethe
europa |
|
|
42 |
Lepidoptera |
Nymphalidae |
Tamil Treebrown |
Lethe
drypetis |
|
|
43 |
Lepidoptera |
Nymphalidae |
Common Treebrown |
Lethe
rohria |
|
|
44 |
Lepidoptera |
Nymphalidae |
Common Bushbrown |
Mycalesis
perseus |
|
|
45 |
Lepidoptera |
Nymphalidae |
Dark Branded Bushbrown * |
Mycalesis
mineus |
|
|
46 |
Lepidoptera |
Nymphalidae |
Gladeye Bushbrown |
Mycalesis
patnia |
|
|
47 |
Lepidoptera |
Nymphalidae |
Medus Brown |
Orsotrianea
medus |
|
|
48 |
Lepidoptera |
Nymphalidae |
Common Three-ring * |
Ypthima
asterope |
|
|
49 |
Lepidoptera |
Nymphalidae |
White Or Ceylon Four-ring * |
Ypthima
ceylonica |
|
|
50 |
Lepidoptera |
Nymphalidae |
Common Four-ring |
Ypthima
huebneri |
|
|
51 |
Lepidoptera |
Nymphalidae |
Common Five-ring |
Ypthima
baldus |
|
|
52 |
Lepidoptera |
Nymphalidae |
Common Nawab * |
Polyura
athamas |
II |
|
53 |
Lepidoptera |
Nymphalidae |
Anomalous Nawab * |
Polyura
agraria |
|
|
54 |
Lepidoptera |
Nymphalidae |
Blue Nawab * |
Polyura
schreiberi |
I |
|
55 |
Lepidoptera |
Nymphalidae |
Tawny Rajah |
Charaxes
bernardus |
II |
|
56 |
Lepidoptera |
Nymphalidae |
Black Rajah * |
Charaxes
solon |
II |
|
57 |
Lepidoptera |
Nymphalidae |
Tawny Coster |
Acraea
violae |
|
|
58 |
Lepidoptera |
Nymphalidae |
Tamil Lacewing |
Cethosia
nietneri |
|
|
59 |
Lepidoptera |
Nymphalidae |
Cruiser |
Vindula erota |
|
|
60 |
Lepidoptera |
Nymphalidae |
Rustic |
Cupha erymanthis |
|
|
61 |
Lepidoptera |
Nymphalidae |
Common Leopard |
Phalanta
phalantha |
|
|
62 |
Lepidoptera |
Nymphalidae |
Small Leopard |
Phalanta
alcippe |
II |
|
63 |
Lepidoptera |
Nymphalidae |
Tamil Yeoman |
Cirrochroa
thais |
|
|
64 |
Lepidoptera |
Nymphalidae |
Black Prince * |
Rohana
parisatis |
|
|
65 |
Lepidoptera |
Nymphalidae |
Painted Courtesan * |
Euripus
consimilis |
II |
|
66 |
Lepidoptera |
Nymphalidae |
Chestnut-Streaked Sailer |
Neptis
jumbah |
|
|
67 |
Lepidoptera |
Nymphalidae |
Common Sailer |
Neptis
hylas |
|
|
68 |
Lepidoptera |
Nymphalidae |
Clear Sailer * |
Neptis
nata |
II |
|
69 |
Lepidoptera |
Nymphalidae |
Shortbanded Sailer * |
Neptis
columella |
I |
|
70 |
Lepidoptera |
Nymphalidae |
Yellow Jack Sailer |
Neptis
viraja |
|
|
71 |
Lepidoptera |
Nymphalidae |
Common Lascar |
Pantoporia
hordonia |
|
|
72 |
Lepidoptera |
Nymphalidae |
Extra Lascar * |
Pantoporia
sandaka |
|
|
73 |
Lepidoptera |
Nymphalidae |
Colour Sergeant |
Athyma
nefte |
|
|
74 |
Lepidoptera |
Nymphalidae |
Staff Sergeant * |
Athyma
selenophora |
II |
|
75 |
Lepidoptera |
Nymphalidae |
Blackvein Sergeant |
Athyma
ranga |
|
|
76 |
Lepidoptera |
Nymphalidae |
Common Sergeant |
Athyma
perius |
|
|
77 |
Lepidoptera |
Nymphalidae |
Commander |
Limenitis
procris |
|
|
78 |
Lepidoptera |
Nymphalidae |
Clipper |
Parthenos
sylvia |
II |
|
79 |
Lepidoptera |
Nymphalidae |
Grey Count |
Tanaecia
lepidea |
II |
|
80 |
Lepidoptera |
Nymphalidae |
Common Baron |
Euthalia
aconthea |
II |
|
81 |
Lepidoptera |
Nymphalidae |
Gaudy Baron |
Euthalia
lubentina |
IV |
|
82 |
Lepidoptera |
Nymphalidae |
Redspot Duke * |
Dolpha
evelina |
II |
|
83 |
Lepidoptera |
Nymphalidae |
Angled Castor |
Ariadne
ariadne |
|
|
84 |
Lepidoptera |
Nymphalidae |
Common Castor |
Ariadne
merione |
|
|
85 |
Lepidoptera |
Nymphalidae |
Common Map |
Cyrestis
thyodamas |
|
|
86 |
Lepidoptera |
Nymphalidae |
Club Beak * |
Libythea myrrha |
|
|
87 |
Lepidoptera |
Nymphalidae |
Yellow Pansy |
Junonia
hierta |
|
|
88 |
Lepidoptera |
Nymphalidae |
Lemon Pansy |
Junonia
lemonias |
|
|
89 |
Lepidoptera |
Nymphalidae |
Peacock Pansy |
Junonia
almana |
|
|
90 |
Lepidoptera |
Nymphalidae |
Grey Pansy |
Junonia
atlites |
|
|
91 |
Lepidoptera |
Nymphalidae |
Chocolate Pansy |
Junonia
iphita |
|
|
92 |
Lepidoptera |
Nymphalidae |
Painted Lady * |
Cynthia
cardui |
|
|
93 |
Lepidoptera |
Nymphalidae |
Great Eggfly |
Hypolimnas
bolina |
|
|
94 |
Lepidoptera |
Nymphalidae |
Danaid Eggfly |
Hypolimnas
misippus |
I
and II |
|
95 |
Lepidoptera |
Nymphalidae |
Autumn leaf (Malabar) |
Doleschallia
bisaltide malabarica |
II |
|
96 |
Lepidoptera |
Nymphalidae |
South Indian Blue Oakleaf |
Kallima
horsfieldi |
II |
|
97 |
Lepidoptera |
Nymphalidae |
Glassy Tiger |
Parantica
aglea |
II |
|
98 |
Lepidoptera |
Nymphalidae |
Blue Tiger |
Tirumala
limniace |
|
|
99 |
Lepidoptera |
Nymphalidae |
Dark Blue Tiger * |
Tirumala
septentrionis |
|
|
100 |
Lepidoptera |
Nymphalidae |
Plain Tiger |
Danaus
chrysippus |
|
|
101 |
Lepidoptera |
Nymphalidae |
Striped Or Common Tiger |
Danaus
genutia |
|
|
102 |
Lepidoptera |
Nymphalidae |
Common Indian Crow |
Euploea
core |
|
|
103 |
Lepidoptera |
Nymphalidae |
Double-Branded Crow * |
Euploea
sylvester |
|
|
104 |
Lepidoptera |
Nymphalidae |
Brown King Crow * |
Euploea
klugii |
|
|
105 |
Lepidoptera |
Nymphalidae |
Malabar Tree Nymph |
Idea
malabarica |
|
|
106 |
Lepidoptera |
Riodinidae |
Double-Banded Judy * |
Abisara
albofasciatus |
|
|
107 |
Lepidoptera |
Lycaenidae |
Apefly * |
Spalgis
epius |
|
|
108 |
Lepidoptera |
Lycaenidae |
Common Pierrot |
Castalius
rosimon |
I |
|
109 |
Lepidoptera |
Lycaenidae |
Angled Pierrot |
Caleta
caleta |
|
|
110 |
Lepidoptera |
Lycaenidae |
Banded Blue Pierrot |
Discolampa
ethion |
|
|
111 |
Lepidoptera |
Lycaenidae |
Dark Pierrot |
Tarucus
ananda |
IV |
|
112 |
Lepidoptera |
Lycaenidae |
Spotted Pierrot * |
Tarucus
nara |
|
|
113 |
Lepidoptera |
Lycaenidae |
Zebra Blue * |
Leptotes
plinius |
|
|
114 |
Lepidoptera |
Lycaenidae |
Common Hedge Blue |
Acytolepis
puspa |
I |
|
115 |
Lepidoptera |
Lycaenidae |
Plain Hedge Blue * |
Celastrina
lavendularis |
|
|
116 |
Lepidoptera |
Lycaenidae |
Quaker |
Neopithecops
zalmora |
|
|
117 |
Lepidoptera |
Lycaenidae |
Malayan |
Magisba
malaya |
|
|
118 |
Lepidoptera |
Lycaenidae |
Dark Grass Blue |
Zizeeria
karsandra |
|
|
119 |
Lepidoptera |
Lycaenidae |
Lesser Grass Blue |
Zizina
otis |
|
|
120 |
Lepidoptera |
Lycaenidae |
Tiny Grass Blue |
Zizula
hylax |
|
|
121 |
Lepidoptera |
Lycaenidae |
Lime Blue |
Chilades
laius |
II |
|
122 |
Lepidoptera |
Lycaenidae |
Plains Cupid |
Chilades
pandava |
|
|
123 |
Lepidoptera |
Lycaenidae |
Grass Jewel * |
Freyeria
trochylus |
|
|
124 |
Lepidoptera |
Lycaenidae |
Gram Blue |
Euchrysops
cnejus |
II |
|
125 |
Lepidoptera |
Lycaenidae |
Forget-Me-Not |
Catochrysops
strabo |
|
|
126 |
Lepidoptera |
Lycaenidae |
Pea Blue * |
Lampides
boeticus |
II |
|
127 |
Lepidoptera |
Lycaenidae |
Dark Cerulean * |
Jamides
bochus |
|
|
128 |
Lepidoptera |
Lycaenidae |
Common Cerulean |
Jamides
celeno |
|
|
129 |
Lepidoptera |
Lycaenidae |
Metallic Cerulean * |
Jamides
alecto |
|
|
130 |
Lepidoptera |
Lycaenidae |
Large 4-Line Blue * |
Nacaduba
pactolus |
II |
|
131 |
Lepidoptera |
Lycaenidae |
Pale 4-Line Blue * |
Nacaduba
hermus |
|
|
132 |
Lepidoptera |
Lycaenidae |
Transparent 6-Line Blue * |
Nacaduba
kurava |
|
|
133 |
Lepidoptera |
Lycaenidae |
Opaque 6-Line Blue * |
Nacaduba
beroe |
|
|
134 |
Lepidoptera |
Lycaenidae |
Common Line Blue * |
Prosotas
nora |
|
|
135 |
Lepidoptera |
Lycaenidae |
Tailless Line Blue * |
Prosotas
dubiosa |
|
|
136 |
Lepidoptera |
Lycaenidae |
Dingy Line Blue * |
Petrolaea
dana |
|
|
137 |
Lepidoptera |
Lycaenidae |
White-Tipped Line Blue * |
Prosotas
noreia |
|
|
138 |
Lepidoptera |
Lycaenidae |
Red Pierrot |
Talicada
nyseus |
|
|
139 |
Lepidoptera |
Lycaenidae |
Common Ciliate Blue * |
Anthene
emolus |
|
|
140 |
Lepidoptera |
Lycaenidae |
Pointed Ciliate Blue |
Anthene
lycaenina |
|
|
141 |
Lepidoptera |
Lycaenidae |
Western Centaur Oakblue * |
Arhopala
pseudocentaurus |
|
|
142 |
Lepidoptera |
Lycaenidae |
Large Oakblue |
Arhopala
amantes |
|
|
143 |
Lepidoptera |
Lycaenidae |
Rosy Or Kanara Oakblue * |
Arhopala
alea |
I |
|
144 |
Lepidoptera |
Lycaenidae |
Aberrant Oakblue * |
Arohopala
abseus |
|
|
145 |
Lepidoptera |
Lycaenidae |
Tamil Oakblue |
Arhopala
bazaloides |
|
|
146 |
Lepidoptera |
Lycaenidae |
Common Acacia Blue * |
Surendra
quercetorum Surendra |
|
|
147 |
Lepidoptera |
Lycaenidae |
Silverstreaked Acacia Blue * |
Zinaspa
todara |
II |
|
148 |
Lepidoptera |
Lycaenidae |
Silverstreak Blue |
Iraota
timoleon |
|
|
149 |
Lepidoptera |
Lycaenidae |
Leaf Blue |
Amblypodia
anita |
|
|
150 |
Lepidoptera |
Lycaenidae |
Common Silverline |
Spindasis
vulcanus |
|
|
151 |
Lepidoptera |
Lycaenidae |
Longbanded Silverline * |
Spindasis
lohita |
II |
|
152 |
Lepidoptera |
Lycaenidae |
Yamfly * |
Loxura
atymnus |
|
|
153 |
Lepidoptera |
Lycaenidae |
Common Imperial |
Cheritra
freja |
|
|
154 |
Lepidoptera |
Lycaenidae |
Monkey Puzzle |
Rathinda
amor |
|
|
155 |
Lepidoptera |
Lycaenidae |
Redspot * |
Zesius
chrysomallus |
|
|
156 |
Lepidoptera |
Lycaenidae |
Silver Royal * |
Ancema
blanka |
|
|
157 |
Lepidoptera |
Lycaenidae |
Broadtail Royal * |
Creon
cleobis |
|
|
158 |
Lepidoptera |
Lycaenidae |
White Royal * |
Pratapa
deva |
II |
|
159 |
Lepidoptera |
Lycaenidae |
Peacock Royal * |
Tajuria
cippus |
II |
|
160 |
Lepidoptera |
Lycaenidae |
Orchid Tit * |
Hypolycaena
othona |
I |
|
161 |
Lepidoptera |
Lycaenidae |
Fluffy Tit * |
Zeltus
amasa |
|
|
162 |
Lepidoptera |
Lycaenidae |
Cornelian * |
Deudorix epijarbas |
|
|
163 |
Lepidoptera |
Lycaenidae |
Common Guava Blue * |
Deudorix
isocrates |
|
|
164 |
Lepidoptera |
Lycaenidae |
Large Guava Blue * |
Deudorix
perse |
|
|
165 |
Lepidoptera |
Lycaenidae |
Plane * |
Bindahara phocides |
II |
|
166 |
Lepidoptera |
Lycaenidae |
Indian Red Flash * |
Rapala
iarbus |
|
|
167 |
Lepidoptera |
Lycaenidae |
Slate Flash |
Rapala
manea |
|
|
168 |
Lepidoptera |
Lycaenidae |
Indigo Flash * |
Rapala
varuna |
II |
|
169 |
Lepidoptera |
Lycaenidae |
Indian Sunbeam |
Curetis
thetis |
|
|
170 |
Lepidoptera |
Lycaenidae |
Shiva Sunbeam * |
Curetis
siva |
|
|
171 |
Lepidoptera |
Lycaenidae |
Malabar Flash * |
Rapala
lankana |
|
|
172 |
Lepidoptera |
Lycaenidae |
Common Onyx |
Horaga
onyx |
II |
|
173 |
Lepidoptera |
Hesperiidae |
Orange-Striped Awl/Orange Awlet
* |
Burara
jaina |
|
|
174 |
Lepidoptera |
Hesperiidae |
Orangetail Awl/Pale Green Awlet
* |
Bibasis
sena |
II |
|
175 |
Lepidoptera |
Hesperiidae |
Common Banded Awl * |
Hasora
chromus |
|
|
176 |
Lepidoptera |
Hesperiidae |
White Banded Awl * |
Hasora
taminatus |
|
|
177 |
Lepidoptera |
Hesperiidae |
Common Awl * |
Hasora
badra |
|
|
178 |
Lepidoptera |
Hesperiidae |
Brown Awl |
Badamia
exclamationis |
|
|
179 |
Lepidoptera |
Hesperiidae |
Common Spotted Flat |
Celaenorrhinus
leucocera |
|
|
180 |
Lepidoptera |
Hesperiidae |
Malabar Spotted Flat * |
Celaenorrhinus
ambareesa |
|
|
181 |
Lepidoptera |
Hesperiidae |
Tamil Spotted Flat * |
Celaenorrhinus
ruficornis |
|
|
182 |
Lepidoptera |
Hesperiidae |
Common/Ceylon Snow Flat * |
Tagiades
jepetus |
|
|
183 |
Lepidoptera |
Hesperiidae |
Water Snow Flat |
Tagiades
litigiosa |
|
|
184 |
Lepidoptera |
Hesperiidae |
Fulvous Pied Flat |
Psuedocoladenia
dan |
|
|
185 |
Lepidoptera |
Hesperiidae |
Tricolour Flat |
Psuedocoladenia
indrana |
|
|
186 |
Lepidoptera |
Hesperiidae |
Common Small Flat |
Sarangesa
dasahara |
|
|
187 |
Lepidoptera |
Hesperiidae |
Spotted Small Flat * |
Sarangesa
purendra |
|
|
188 |
Lepidoptera |
Hesperiidae |
Angled Flat/Black Angle |
Tapena
twaithesi |
|
|
189 |
Lepidoptera |
Hesperiidae |
Golden Angle |
Odontoptilum
ransonnetti |
|
|
190 |
Lepidoptera |
Hesperiidae |
Indian Grizzled/Indian Skipper * |
Spialia
galba |
|
|
191 |
Lepidoptera |
Hesperiidae |
Pygmy Grass-/Scrub-Hopper * |
Aeromachus
pygmaeus |
|
|
192 |
Lepidoptera |
Hesperiidae |
Bush Hopper * |
Ampittia
dioscorides |
|
|
193 |
Lepidoptera |
Hesperiidae |
Indian Ace * |
Halpe
homolea |
II |
|
194 |
Lepidoptera |
Hesperiidae |
Madras Ace |
Thoressa
honorei |
IV |
|
195 |
Lepidoptera |
Hesperiidae |
Moore’s Ace * |
Halpe
porus |
|
|
196 |
Lepidoptera |
Hesperiidae |
Chestnut Bob |
Lambrix
salsala |
|
|
197 |
Lepidoptera |
Hesperiidae |
Coon |
Psolos fuligo |
|
|
198 |
Lepidoptera |
Hesperiidae |
Common Banded Demon |
Notocrypta
paralysos |
|
|
199 |
Lepidoptera |
Hesperiidae |
Restricted Demon |
Notocrypta
curvifascia |
|
|
200 |
Lepidoptera |
Hesperiidae |
Grass Demon |
Udaspes
folus |
|
|
201 |
Lepidoptera |
Hesperiidae |
Indian Palm Bob * |
Suastus
gremius |
|
|
202 |
Lepidoptera |
Hesperiidae |
Tree Flitter * |
Hyarotis
adrastus |
IV |
|
203 |
Lepidoptera |
Hesperiidae |
Giant Redeye |
Gangara
thyrsis |
|
|
204 |
Lepidoptera |
Hesperiidae |
Common Redeye * |
Matapa
aria |
|
|
205 |
Lepidoptera |
Hesperiidae |
Tamil Grass Dart |
Taractrocera
ceramas |
|
|
206 |
Lepidoptera |
Hesperiidae |
Pale Palm Dart * |
Telicota
colon |
|
|
207 |
Lepidoptera |
Hesperiidae |
Plain Palm Dart * |
Cephrenes
acalle |
|
|
208 |
Lepidoptera |
Hesperiidae |
African Straight/Straight Swift
* |
Parnara
naso |
|
|
209 |
Lepidoptera |
Hesperiidae |
Bevan's Swift * |
Borbo
bevani |
|
|
210 |
Lepidoptera |
Hesperiidae |
Dark Small-Branded Swift * |
Pelopidas
mathias |
|
|
211 |
Lepidoptera |
Hesperiidae |
Conjoined Swift * |
Pelopidas
conjucta |
|
|
212 |
Lepidoptera |
Hesperiidae |
Paintbrush Swift * |
Baoris
farri |
IV |
|
213 |
Lepidoptera |
Hesperiidae |
Blank Swift * |
Caltoris
kumara |
|
|
214 |
Lepidoptera |
Hesperiidae |
Philippine Swift * |
Caltoris
philippina |
II |
|
215 |
Lepidoptera |
Hesperiidae |
Maculate Lancer * |
Salanoemia
sala |
|
|
216 |
Lepidoptera |
Hesperiidae |
Small Palm Bob * |
Suastus
minutus |
|
|
217 |
Lepidoptera |
Hesperiidae |
Wax Dart * |
Cupitha
purreea |
|
|
218 |
Lepidoptera |
Hesperiidae |
Common Dartlet |
Oriens
goloides |
|
Source:
India Biodiversity Portal (https://indiabiodiversity.org/checklist/show/228);
Rangnekar & Dharwadkar (2009); *Direct Sightings by Parag Rangnekar, Omkar
Dharwadkar & Ravindra Bhambure
Appendix
VI. Odonates of Bhagwan Mahavir Wildlife Sanctuary and National Park.
|
|
Common
name |
Scientific
name |
Family |
IUCN
status |
Western
Ghat Endemism |
|
1 |
Pale Dartlet |
Agriocnemis
pieris |
Coenagrionidae |
|
|
|
2 |
Pygmy Dartlet |
Agriocnemis
pygmea |
Coenagrionidae |
|
|
|
3 |
Splendid Dartlet |
Agriocnemis
splendissima |
Coenagrionidae |
|
|
|
4 |
Orange-tailed Marsh Dart |
Ceriagrion
cerinorubellum |
Coenagrionidae |
|
|
|
5 |
Coromandel Marsh Dart |
Ceriagrion
coromandelianum |
Coenagrionidae |
|
|
|
6 |
Rusty Marsh Dart |
Ceriagrion
olivaceum |
Coenagrionidae |
|
|
|
7 |
Sindhudurg Marsh Dart |
Ceriagrion
chromothorax |
Coenagrionidae |
|
|
|
8 |
Rusty Marsh Dart |
Ceriagrion
olivaceum |
Coenagrionidae |
|
|
|
9 |
Golden Dartlet |
Ischnura
rubilio |
Coenagrionidae |
|
|
|
10 |
Pygmy Bluespot |
Mortonagrion
varralli |
Coenagrionidae |
|
Endemic |
|
11 |
Yellow-striped Blue Dart |
Pseudagrion
indicum |
Coenagrionidae |
|
Endemic |
|
12 |
Saffron-faced Blue Dart |
Pseudagrion
rubriceps |
Coenagrionidae |
|
|
|
13 |
Yellow Bush Dart |
Copera
marginipes |
Platycenemididae |
|
|
|
14 |
Blue Bush Dart |
Copera
vittata |
Platycenemididae |
|
|
|
15 |
Pied Reedtail |
Protosticta
gravelyi |
Platystictidae |
|
Endemic |
|
16 |
Red-spot Reedtail |
Protosticta
sanguinostigma |
Platystictidae |
Vulnerable |
Endemic |
|
17 |
Black Bambootail |
Prodasineura
verticalis |
Platycenemididae |
|
|
|
18 |
Blackwinged Bambootail |
Disparoneura
quadrimaculata |
Platycenemididae |
|
|
|
19 |
Coorg Bambootail * |
Caconeura
ramburi |
Platycenemididae |
|
|
|
20 |
Black & yellow bambootail |
Elattoneura
tetrica |
Platycenemididae |
|
Endemic |
|
21 |
Emerald Spreadwing |
Lestes
elatus |
Lestidae |
|
|
|
22 |
Stream Glory |
Neurobasis
chinensis |
Calopterygidae |
|
|
|
23 |
Black-tipped Forest Glory |
Vestalis
apicalis |
Calopterygidae |
|
|
|
24 |
Clear-winged Forest Glory |
Vestalis
gracilis |
Calopterygidae |
|
|
|
25 |
River Heliodor |
Libellago
indica |
Chlorocyphidae |
|
Endemic |
|
26 |
Stream Ruby |
Rhinocypha
bisignata |
Chlorocyphidae |
|
|
|
27 |
Malabar Torrent Dart |
Euphaea
fraseri |
Euphaeidae |
|
Endemic |
|
28 |
Black Torrent Dart |
Dysphaea
ethela |
Euphaeidae |
|
Endemic |
|
29 |
Plain sinuate Clubtail |
Burmagomphus
laidlawi |
Gomphidae |
|
Endemic |
|
30 |
|
Cyclogomphus
flavoannulatus |
Gomphidae |
|
Endemic |
|
31 |
Kodagu Clubtail |
Gomphidia
kodaguensis |
Gomphidae |
|
Endemic |
|
32 |
Forest Hooktail |
Heliogomphus
promelas |
Gomphidae |
Near Threatened |
|
|
33 |
Wayanad Bowtail |
Macrogomphus
wynaadicus |
Gomphidae |
|
Endemic |
|
34 |
Common Clubtail |
Ictinogomphus
rapax |
Gomphidae |
|
|
|
35 |
Giant Clubtail |
Megalogomphus
hannyngtoni |
Gomphidae |
Near Threatened |
|
|
36 |
Long-legged Clubtail |
Merogomphus
longistigma |
Gomphidae |
|
Endemic |
|
37 |
Pigmy Clubtail |
Microgomphus
souteri |
Gomphidae |
|
Endemic |
|
38 |
Laidlaw's Clubtail |
Onychogomphus
acinaces |
Gomphidae |
|
Endemic |
|
39 |
Commmon Hooktail |
Paragomphus
lineatus |
Gomphidae |
|
|
|
40 |
Blue-tailed Green Darner |
Anax
guttatus |
Aeshnidae |
|
|
|
41 |
Blue Darner * |
Anax
immaculifrons |
Aeshnidae |
|
|
|
42 |
Brown Darner |
Gynacantha
dravida |
Aeshnidae |
|
|
|
43 |
Parakeet Darner |
Gynacantha
bayadera |
Aeshnidae |
|
|
|
44 |
Common River Hawk |
Epophthalmia
vittata |
Macromidae |
|
|
|
45 |
|
Macromia
flavicincta |
Macromidae |
|
|
|
46 |
|
Macromia
irata |
Macromidae |
|
Endemic |
|
47 |
Evening Torrent Hawk |
Idionyx
saffronata |
Cordulidae |
|
Endemic |
|
48 |
Goan Shadowdancer |
Idionyx
gomantakensis |
Cordulidae |
|
Endemic |
|
49 |
Ditch Jewel |
Brachythemis
contaminata |
Libellulidae |
|
|
|
50 |
Granite Ghost * |
Bradinopyga
geminata |
Libellulidae |
|
|
|
51 |
Konkan Rock Dweller * |
Bradinopyga
konkanensis |
Libellulidae |
|
|
|
52 |
Emerald-banded Skimmer |
Cratilla
lineata |
Libellulidae |
|
|
|
53 |
Ruddy Marsh Skimmer |
Crocothemis
servilia |
Libellulidae |
|
|
|
54 |
Ground Skimmer |
Diplacodes
trivialis |
Libellulidae |
|
|
|
55 |
Amber-winged Glider |
Hydrobasileus
croceus |
Libellulidae |
|
|
|
56 |
Blue Hawklet |
Hylaeothemis
indica |
Libellulidae |
|
|
|
57 |
Dark Ground Skimmer |
Indothemis
carnatica |
Libellulidae |
Near Threatened |
|
|
58 |
Asian Bloodtail |
Lathrecista
asiatica |
Libellulidae |
|
|
|
59 |
Fulvous Forest Skimmer |
Neurothemis
fulvia |
Libellulidae |
|
|
|
60 |
Pale Forest Skimmer |
Neurothemis
intermedia |
Libellulidae |
|
|
|
61 |
Pied Paddy Skimmer |
Neurothemis
tullia |
Libellulidae |
|
|
|
62 |
Stellate River Hawk * |
Onychothemis
testacea |
Libellulidae |
|
|
|
63 |
Cherry Skimmer |
Orthetrum
chrysis |
Libellulidae |
|
|
|
64 |
Blue Marsh Hawk |
Orthetrum
glaucum |
Libellulidae |
|
|
|
65 |
Crimson-tailed Marsh Hawk |
Orthetrum
pruinosum |
Libellulidae |
|
|
|
66 |
Blue-eyed Marsh Hawk |
Orthetrum
luzonicum |
Libellulidae |
|
|
|
67 |
Green Marsh Hawk |
Orthetrum
sabina |
Libellulidae |
|
|
|
68 |
Tiny Flufftail * |
Palpopleura
sexmaculata |
Libellulidae |
|
|
|
69 |
Wandering Glider |
Pantala
flavescens |
Libellulidae |
|
|
|
70 |
Yellow-tailed Ashy Skimmer |
Potamarcha
congener |
Libellulidae |
|
|
|
71 |
Common Picturewing |
Rhyothemis
variegata |
Libellulidae |
|
|
|
72 |
Pigmy Skimmer |
Tetrathemis
platyptera |
Libellulidae |
|
|
|
73 |
Coral-tailed Cloud-wing * |
Tholymis
tillarga |
Libellulidae |
|
|
|
74 |
Red Marsh Trotter |
Tramea
basilaris |
Libellulidae |
|
|
|
75 |
Black Marsh Trotter |
Tramea
limbata |
Libellulidae |
|
|
|
76 |
Crimson Marsh Glider |
Trithemis
aurora |
Libellulidae |
|
|
|
77 |
Black Stream Glider |
Trithemis
festiva |
Libellulidae |
|
|
|
78 |
Long-legged Marsh Glider * |
Trithemis
pallidinervis |
Libellulidae |
|
|
|
79 |
Iridescent Stream Glider * |
Zygonyx
iris |
Libellulidae |
|
|
|
80 |
Brown Dusk Hawk |
Zyxomma
petiolatum |
Libellulidae |
|
|
Compiled
from: Prasad & Varshney (1995); Rangnekar et al. (2010); Rangnekar &
Naik (2014); Rangnekar et al. (2019); Subramanian et al. (2013); direct sightings (indicated by *) by Parag
Rangnekar, Omkar Dharwadkar, Rohan Naik, Sridhar Halali, & Dhiraj Halali.
Appendix
VII. Checklist of reptiles in Bhagwan Mahavir Wildlife Sanctuary and National
Park.
|
|
Order |
Family |
Species |
Common
name |
IUCN
Red List category |
WPA
schedule |
|
1 |
Testudines |
Bataguridae |
Melanochelys
trijuga |
Indian Black Turtle |
Near Threatened |
|
|
2 |
Testudines |
Trionychidae |
Lissemys
punctata |
Indian Flapshell Turtle |
Least Concern |
I |
|
3 |
Squamata |
Gekkonidae |
Cnemaspis
goaensis |
Goan Day Gecko |
Endangered |
|
|
4 |
Squamata |
Gekkonidae |
Cyrtodactylus
albofasciatus |
Boulenger’s Indian Gecko |
Not Evaluated |
|
|
5 |
Squamata |
Gekkonidae |
Hemidactylus
frenatus |
Asian House Geck |
Least Concern |
|
|
6 |
Squamata |
Gekkonidae |
Hemidactylus
prashadi |
Prashad’s Gecko |
Least Concern |
|
|
7 |
Squamata |
Lacertidae |
Ophisops
beddomei |
Beddome’s Snake-eyed Lizard |
Least Concern |
|
|
8 |
Squamata |
Mabuyidae |
Allapalli
grass skink |
Allapalli Grass Skink |
Least Concern |
|
|
9 |
Squamata |
Mabuyidae |
Eutropis
macularia |
Bronze Grass Skink |
Least Concern |
|
|
10 |
Squamata |
Mabuyidae |
Eutropis
carinata |
Common Keeled Skink |
Least Concern |
|
|
11 |
Squamata |
Lygosomidae |
Lygosoma
goaensis |
Goan Supple Skink |
Least Concern |
|
|
12 |
Squamata |
Lygosomidae |
Lygosoma
punctatum |
Spotted Supple Skink |
Least Concern |
|
|
13 |
Squamata |
Varanidae |
Varanus
bengalensis |
Bengal Monitor Lizard |
Least Concern |
|
|
14 |
Squamata |
Chamaeleonidae |
Chamaeleo
zeylanicus |
Indian Chamaeleon |
Least Concern |
II |
|
15 |
Squamata |
Agamidae |
Calotes
rouxii |
Roux’s Forest Lizard |
Least Concern |
|
|
16 |
Squamata |
Agamidae |
Calotes
versicolor |
Indian Garden Lizard |
Least Concern |
|
|
17 |
Squamata |
Agamidae |
Draco
dussumieri |
South Indian Flying Lizard |
Least Concern |
|
|
18 |
Squamata |
Typhlopidae |
Indotyphlops
braminus |
Brahminy Worm Snake |
Least Concern |
|
|
19 |
Squamata |
Typhlopidae |
Grypotyphlops
acutus |
Beaked Worm Snake |
Least Concern |
|
|
20 |
Squamata |
Erycidae |
Eryx
whitakeri |
Whitaker’s Boa |
Least Concern |
|
|
21 |
Squamata |
Uropeltidae |
Melanophidium
khairei |
Khaire’s Shieldtail |
Least Concern |
|
|
22 |
Squamata |
Uropeltidae |
Uropeltis
beddomii |
Beddome’s Shieldtail |
Least Concern |
|
|
23 |
Squamata |
Pythonidae |
Python
molurus |
Rock Python |
Near Threatened |
I |
|
24 |
Squamata |
Viperidae |
Daboia
russelii |
Russell’s Viper |
Least Concern |
II |
|
25 |
Squamata |
Viperidae |
Echis
carinatus carinatus |
Indian Saw-scaled Viper |
Not Evaluated |
|
|
26 |
Squamata |
Viperidae |
Hypnale
hypnale |
Common Hump-nosed Pit Viper |
Not Evaluated |
|
|
27 |
Squamata |
Viperidae |
Trimeresurus
gramineus |
Bamboo Pit Viper |
Least Concern |
|
|
28 |
Squamata |
Viperidae |
Trimeresurus
malabaricus |
Malabar Pit Viper |
Least Concern |
|
|
29 |
Squamata |
Elapidae |
Bungarus
caeruleus |
Common Indian Krait |
Not Evaluated |
|
|
30 |
Squamata |
Elapidae |
Calliophis
castoe |
Castoe’s Coral Snake |
Not Evaluated |
|
|
31 |
Squamata |
Elapidae |
Calliophis
melanurus |
Slender Coral Snake |
Not Evaluated |
|
|
32 |
Squamata |
Elapidae |
Naja
naja |
Spectacled Cobra |
Least Concern |
II |
|
33 |
Squamata |
Elapidae |
Ophiophagus
hannah |
King Cobra |
Vulnerable |
II |
|
34 |
Squamata |
Natricidae |
Amphiesma
stolatum |
Striped Keelback |
Not Evaluated |
|
|
35 |
Squamata |
Natricidae |
Atretium
schistosum |
Olive Keelback Water Snake |
Least Concern |
|
|
36 |
Squamata |
Natricidae |
Hebius
beddomei |
Beddome’s Keelback |
Least Concern |
|
|
37 |
Squamata |
Natricidae |
Macrophistodon
plumbicolor |
Green Keelback |
Not Evaluated |
|
|
38 |
Squamata |
Natricidae |
Rhabdops aquaticus |
Aquatic Forest Snake |
Not Evaluated |
|
|
39 |
Squamata |
Natricidae |
Xenochrophis
piscator |
Checkered Keelback |
Not Evaluated |
II |
|
40 |
Squamata |
Colubridae |
Ahaetulla
nasuta |
Common Vine Snake |
Not Evaluated |
|
|
41 |
Squamata |
Colubridae |
Ahaetulla
pulverulenta |
Brown Vine Snake |
Least Concern |
|
|
42 |
Squamata |
Colubridae |
Boiga
beddomei |
Beddome’s Cat Snake |
Data Deficient |
|
|
43 |
Squamata |
Colubridae |
Boiga
forsteni |
Forsten's Cat Snake |
Least Concern |
|
|
44 |
Squamata |
Colubridae |
Chrysopelea
ornata ornata |
Ornate Flying Snake |
Not Evaluated |
|
|
45 |
Squamata |
Colubridae |
Coelognathus
helena monticollaris |
Montane Trinket Snake |
Not Evaluated |
|
|
46 |
Squamata |
Colubridae |
Dendrelaphis
ashoki |
Ashok’s Bronzeback Snake |
Least Concern |
|
|
47 |
Squamata |
Colubridae |
Dendrelaphis
tristis |
Common Bronzeback Snake |
Not Evaluated |
|
|
48 |
Squamata |
Colubridae |
Boiga
forsteni |
Forsten's Cat Snake |
Least Concern |
|
|
49 |
Squamata |
Colubridae |
Lycodon
aulicus |
Common Wolf Snake |
Not Evaluated |
|
|
50 |
Squamata |
Colubridae |
Oligodon
taeniolatus fasciatus |
Russell’s Kukri Snake |
Least Concern |
|
|
51 |
Squamata |
Colubridae |
Ptyas
mucosa |
Indian Rat Snake |
Not Evaluated |
II |
|
52 |
Crocodylia |
Crocodylidae |
Crocodylus
palustris |
Mugger or Marsh Crocodile |
Vulnerable |
I |
Source: Aengals et al. (2018);
Sharma (1976).
Appendix
VIII. Checklist of amphibians in Bhagwan Mahavir Wildlife Sanctuary and National
Park.
|
|
Order |
Family |
Species |
Common
name |
IUCN
Red List category |
WPA
schedule |
|
1 |
Anura |
Bufonidae |
Duttaphrynus
melanostictus |
Asian Common Toad |
Least Concern |
|
|
2 |
Anura |
Bufonidae |
Duttaphrynus
stomaticus |
Indian Marbled Toad |
Least Concern |
|
|
3 |
Anura |
Bufonidae |
Pedostibes
tuberculosus |
Malabar Tree Toad |
Endangered |
|
|
4 |
Anura |
Dicroglossidae |
Euphlyctis
cyanophlyctis |
Indian Skipper Frog |
Least Concern |
|
|
5 |
Anura |
Dicroglossidae |
Minervarya
rufescens* |
Malabar Wart Frog |
Least Concern |
|
|
6 |
Anura |
Dicroglossidae |
Minervarya
syhadrensis* |
Small Cricket Frog |
Endangered |
|
|
7 |
Anura |
Dicroglossidae |
Minervarya
gomantaki* |
|
|
|
|
8 |
Anura |
Dicroglossidae |
Minervarya
goemchi* |
|
|
|
|
9 |
Anura |
Dicroglossidae |
Minervarya
cepfi* |
|
|
|
|
10 |
Anura |
Dicroglossidae |
Minervarya
agricola* |
|
|
|
|
11 |
Anura |
Dicroglossidae |
Hoplobatrachus
tigerinus |
Indian Bull Frog |
Least Concern |
Schedule IV |
|
12 |
Anura |
Dicroglossidae |
Sphaerotheca
breviceps |
Indian Burrowing Frog |
Least Concern |
|
|
13 |
Anura |
Dicroglossidae |
Sphaerotheca
dobsonii |
Dobson's Burrowing Frog |
Least Concern |
|
|
14 |
Anura |
Microhylidae |
Microhyla
ornata |
Ornate Narrow-mouthed Frog |
Least Concern |
|
|
15 |
Anura |
Microhylidae |
Microhyla
nilphamariensis |
Niphamarai Narrow-mouthed Frog |
Not Evatuated |
|
|
16 |
Anura |
Microhylidae |
Uperodon
globulosus |
Indian Balloon Frog |
Least Concern |
|
|
17 |
Anura |
Microhylidae |
Uperodon
mormoratus |
Indian Dot Frog |
Endangered |
|
|
18 |
Anura |
Nyctibatrachidae |
Nyctibatrachus
danieli |
Daniel's Night Frog |
Least Concern |
|
|
19 |
Anura |
Nyctibatrachidae |
Nyctibatrachus
petraeus |
Castle Rock Night Frog |
Least Concern |
|
|
20 |
Anura |
Ranixalidae |
Indirana
chiravasi |
Amboli Leaping Frog |
Not Evatuated |
|
|
21 |
Anura |
Ranixalidae |
Indirana
salelkari |
Leaping Frog |
Not Evatuated |
|
|
22 |
Anura |
Rhacophoridae |
Pseudophilautus
amboli |
Amboli Bush Frog |
Critically Endangered |
|
|
23 |
Anura |
Rhacophoridae |
Philautus
bombayensis |
Maharashtra Bush Frog |
Vulnerable |
|
|
24 |
Anura |
Racophoridae |
Polypedates
maculatus |
Common Indian Tree Frog |
|
|
|
25 |
Anura |
Rhacophoridae |
Rhacophorus
malabaricus |
Malabar Gliding Frog |
Least Concern |
|
|
26 |
Anura |
Rhacophoridae |
Raorchestes
bombayensis |
Maharashtra Bush Frog |
|
|
|
27 |
Anura |
Ranidae |
Hydrophylax
malabaricus |
Fungoid Frog |
Least Concern |
|
|
28 |
Anura |
Ranidae |
Hydrophylax
bahuvistara |
Wide-spread Fungoid Frog |
|
|
|
29 |
Anura |
Ranidae |
Indosylvirana
temporalis |
Bronzed Frog |
Near Threatened |
|
|
30 |
Anura |
Ranidae |
Indosylvirana
caesari |
Maharashtra Golden-backed Frog |
|
|
|
31 |
Anura |
Ranidae |
Clinotarsus
curtipes |
Bicoloured Frog |
Near Threatened |
|
|
32 |
Anura |
Micrixalidae |
Micrixalus
uttaraghati |
Northern Dancing Frog |
|
|
|
33 |
Gymnophiona |
Ichthyophiidae |
Ichthyophis
davidi |
Chorla Striped Caecilian |
|
|
|
34 |
Gymnophiona |
Ichthyophiidae |
Ichthyophis
bombayensis |
Bombay Caecilian |
Least Concern |
|
|
35 |
Gymnophiona |
Indotyphlidae |
Gegeneophis
danieli |
Daniel’s Ceacilian |
|
|
|
36 |
Gymnophiona |
Indotyphlidae |
Gegeneophis
mhadeiensis |
Mhadei Caecilian |
|
|
*Genus Minervarya used
provisionally. Freshwater Frogs are
mentioned in Schedule IV.
Source: Dinesh et al. (2020);
Kulkarni et al. (2013); Gosavi et al. (2020)
Appendix
IX. Ants of Bhagwan Mahavir Wildlife Sanctuary and National Park.
|
|
Species |
|
|
AMBLYOPONINAE |
|
1 |
Mystrium
sp. |
|
2 |
Stigmatomma
sp. |
|
|
DOLICHODERINAE
|
|
3 |
Tapinoma
indicum Forel, 1895 |
|
4 |
Tapinoma
melanocephalum (Fabricius, 1793) |
|
5 |
Technomyrmex
albipes (Smith, 1861) |
|
|
DORYLINAE
|
|
6 |
Aenictus
ceylonicus (Mayr, 1866) |
|
7 |
Dorylus
orientalis Westwood, 1835 |
|
8 |
Ooceraea
biroi Forel, 1907 |
|
9 |
Parasyscia
aitkenii Forel, 1900 |
|
10 |
Parasyscia
indica Brown, 1975 (E) |
|
|
FORMICINAE
|
|
11 |
Anoplolepis
gracilipes (Smith, 1857) (I) |
|
12 |
Camponotus
angusticollis (Jerdon, 1851) |
|
13 |
Camponotus
compressus (Fabricius, 1787) |
|
14 |
Camponotus
irritans (Smith, 1857) |
|
15 |
Camponotus
parius Emery, 1889 |
|
16 |
Camponotus
radiates Forel, 1892 (E) |
|
17 |
Camponotus
sericeus (Fabricius, 1798) |
|
18 |
Lepisiota
capensis (Mayr, 1862) |
|
19 |
Lepisiota
opaca (Forel, 1892) |
|
20 |
Oecophylla
smaragdina (Fabricius, 1775) |
|
21 |
Paratrechina
longicornis (Latreille, 1802) (I) |
|
22 |
Polyrhachis
exercita (Walker, 1859) |
|
23 |
Polyrhachis
illaudata Walker, 1859 |
|
24 |
Polyrhachis
lacteipennis Smith, 1858 |
|
25 |
Polyrhachis
rastellata (Latreille, 1802) |
|
26 |
Polyrhachis
scissa (Roger,
1862) |
|
27 |
Polyrhachis
tibialis Smith, 1858 |
|
|
MYRMICINAE |
|
28 |
Aphaenogaster
beccarii Emery, 1887 |
|
29 |
Carebara
affinis (Jerdon, 1851) |
|
30 |
Carebara
diversa (Jerdon, 1851) |
|
31 |
Cataulacus
latus Forel, 1891 |
|
32 |
Cataulacus
taprobanae Smith, 1853 |
|
33 |
Crematogaster
dalyi Forel, 1902 |
|
34 |
Crematogaster
rogenhoferi Mayr, 1879 |
|
35 |
Crematogaster
rothneyi Mayr, 1879 |
|
36 |
Crematogaster
subnuda Mayr, 1879 |
|
37 |
Lophomyrmex
quadrispinosus (Jerdon, 1851) |
|
38 |
Meranoplus
bellii Forel, 1902 |
|
39 |
Meranoplus
bicolor (Guerin-Meneville, 1844) |
|
40 |
Monomorium
atomum Forel, 1902 |
|
41 |
Monomorium
dichroum Forel, 1902 |
|
42 |
Monomorium
indicum Forel, 1902 |
|
43 |
Monomorium
pharaonis (Linnaeus, 1758) (I) |
|
44 |
Myrmicaria
brunnea Saunders, 1842 |
|
45 |
Pheidole
grayi Forel, 1902 (E) |
|
46 |
Pheidole
sharpi Forel, 1902 |
|
47 |
Solenopsis
geminata (Fabricius, 1804) (I) |
|
48 |
Strumigenys
hostilis Bolton, 2000 (E) |
|
49 |
Strumigenys
peraucta Bolton, 2000 (E) |
|
50 |
Tetramorium
mixtum Forel, 1902 |
|
51 |
Tetramorium
rugigaster Bolton, 1977 (E) |
|
52 |
Tetramorium
simillimum (Smith, 1851) (I) |
|
53 |
Tetramorium
wroughtonii (Forel, 1902) |
|
54 |
Trichomyrmex
destructor (Jerdon, 1851) (I) |
|
55 |
Trichomyrmex
wroughtoni Forel, 1902 |
|
|
PONERINAE |
|
56 |
Anochetus
graeffei Mayr, 1870 |
|
57 |
Anochetus
(cf) pupulatus Brown, 1978 |
|
58 |
Bothroponera
henryi Donisthorpe, 1942 (E) |
|
59 |
Bothroponera
sulcata (Mayr, 1867) |
|
60 |
Bothroponera
tesseronoda (Emery, 1877) |
|
61 |
Brachyponera
luteipes (Mayr, 1862) |
|
62 |
Diacamma
indicum Santschi,
1920 |
|
63 |
Diacamma
ceylonense Emery, 1897 |
|
64 |
Diacamma
rugosum (Le Guillou, 1842) |
|
65 |
Harpegnathos
saltator Jerdon, 1851 |
|
66 |
Leptogenys
diminuta (Smith, 1857) |
|
67 |
Leptogenys
chinensis (Mayr, 1870) |
|
68 |
Leptogenys
processionalis (Jerdon, 1851) |
|
69 |
Odontomachus
simillimus Smith, 1858 |
|
70 |
Parvaponera
darwinii (Forel, 1893) |
|
71 |
Platythyrea
parallela (Smith, 1859) |
|
72 |
Pseudoneoponera
rufipes (Jerdon, 1851) |
|
|
PSEUDOMYRMECINAE |
|
73 |
Tetraponera
allaborans (Walker, 1859) |
|
74 |
Tetraponera
nigra (Jerdon, 1851) |
|
75 |
Tetraponera
rufonigra (Jerdon, 1851) |