Journal of
Threatened Taxa | www.threatenedtaxa.org | 26 November 2018 | 10(13):
12805–12816
Avian fauna of Amboli Ghat,
Sindhudurg District, Maharashtra State, India
Varun Satose 1,
Vikrant Choursiya 2, Rakesh Deulkar 3 & Sasikumar Menon 4
1,4 Institute for Advanced Training and
Research in Interdisciplinary Sciences, Sion, Mumbai,
Maharashtra 400022, India
2 Zoology Department,
Bhavan’s College, Andheri,
Mumbai, Maharashtra 400058, India
3 No. 87, Amboli
(Bazaar), Sawantwadi, Sindhudurg,
Maharashtra 416510, India
1 vari.devil@gmail.com, 2 madscientist.wilderness@gmail.com
(corresponding author), 3 rakeshdeulkar5@gmail.com, 4 spmtdmlab@gmail.com
doi: https://doi.org/10.11609/jott.2886.10.13.12805-12816 | ZooBank:
urn:lsid:zoobank.org:pub:36EC754D-945F-4C19-9DF4-13EA9DA86E5F
Editor: R. Jayapal,
SACON, Coimbatore, India. Date
of publication: 26 November 2018 (online & print)
Manuscript details: Ms
# 2886 | Received 19 March 2017 | Final received 23 October 2018 | Finally
accepted 31 October 2018
Citation: Satose, V., V. Choursiya,
R. Deulkar & S. Menon (2018). Avian fauna of Amboli Ghat, Sindhudurg District, Maharashtra State, India. Journal
of Threatened Taxa 10(13): 12805–12816; https://doi.org/10.11609/jott.2886.10.13.12805-12816
Copyright: © Satose et al. 2018. Creative Commons Attribution 4.0
International License. JoTT allows unrestricted use
of this article in any medium, reproduction and distribution by providing
adequate credit to the authors and the source of publication.
Funding: It was a self funded project. No funding agency involved.
Competing interests: The authors declare no competing interests.
Acknowledgements: We would like to thank Dr. Parvish Pandya, Pranad Patil, Shashank Dalvi, and Saurabh Sawant for their valuable contributions towards the
checklist and preparation of the manuscript.
We would also like to thank Hemant Ogale and Malabar Nature Conservation Club for their
immense help during the fieldwork in the study area.
Abstract: The present report puts forth a systematic checklist of bird
species observed at Amboli Ghat
in Maharashtra from 2009 to 2012, along with information on their status. A total of 208 species were recorded, which
is around 15% of bird species of the Indian subcontinent. A family-wise analysis showed that the
families Accipitridae and Muscicapidae
(14 species each) followed by Ardeidae dominated the
avifauna of the region. The study also
revealed that the area consisted of 11 species of birds that are classified
under Near Threatened category and two under Vulnerable
category of IUCN. This study highlights
the urgent need to conserve the biodiversity-rich area of Amboli
Ghat with long-term plans.
Keywords: Amboli, avian fauna, diversity, endemic,
Western Ghats.
The Western
Ghats along the western coast of peninsular India is one of the most
ecologically significant biological regions of the world. These hill ranges are recognized as a unique
biogeographic province (Mani 1974), a global biodiversity hotspot (Myers et al.
2000), and as one of the 200 most important eco-regions of the world (Olson
& Dinerstein 1998). Amboli Ghat lies in the Sahyadri Hills
of the Western Ghats in the Sindhudurg District of
Maharashtra State, India. It is located
at 15.9620N–73.9970E and has an average altitude of
approximately 690m. The highest point is
1,100m and the lowest point is 166m. The
terrain is undulating with steep escarpments and dense forests. There are three well-defined seasons in Amboli: the monsoon spanning from June to around
mid-November, the winter from mid-November to February, and the summer, from
March to May. It is the wettest place in
Maharashtra State with an average annual precipitation of 7500mm. The plant life in Amboli
is extremely rich since the climatic conditions give rise to a wide range of
habitats. The habitats range from the
tropical semi-evergreen forests, tropical moist deciduous forests, subtropical
broadleaf hill forests, tropical dry deciduous forests, tropical thorn
vegetation, grasslands, and agricultural lands to wetlands. The wetlands are mainly formed by the
collection of water from streams in abandoned agricultural lands. In general, the vegetation turns drier as one
moves from west to east (into the rain shadow region) across the hills. Lower elevations on the eastern region
receive less than 1,200mm of annual rainfall and contain tropical dry deciduous
and thorny forests, with tropical moist deciduous forests in more well-watered areas (Champion & Seth 1968). With an increase in elevation, tropical
semi-evergreen rainforests appear along the higher slopes and ridges. The western region of the hills tends to have
mostly tropical moist deciduous forests with wet evergreen forests at lower
elevations. The former gives way to the
latter type as one climbs higher. The
forest is mainly fragmented and the semi-evergreen forest patches occur in
isolated pockets.
In less than five years, four new faunal species were
described and reported from Amboli. A species of toad, Xanthophryne tigerinus, was recently
described as endemic to Amboli (Biju
et al. 2009). Amboli
was reported as one of the type localities of a species of frog Pseudophilautes amboli (Biju & Bossuyt 2009), a new species of
coral snake Calliophis castoe
(Smith et al. 2012), and a new species of colubrid
Dendrelaphis girii (Vogel & Rooijen
2011) . Other snakes like Ornate Flying Snake and
Brown Vine Snake were also sighted in this region.
Birds are considered
as useful biological indicators because they are ecologically versatile and
live in all kinds of habitats. Extensive
documentation of avian fauna of various regions of the Western Ghats and
Maharashtra are available. Prasad (2003)
listed about 450 bird species from western Maharashtra, Abdulali
(1981) listed 540 bird species from Maharashtra, and Gole
(1998) studied bird species of Sahyadri,; documentation can also be found in Ranjit
et al. (1990), Lainer (2004), Padhye
et al. (2007), Lawate & Mule (2008), and Kachare et al. (2011).
A systematic study on the avian fauna of Amboli
Ghat is wanting.
The aim of our study was to explore the nature of bird assemblage in
various macrohabitat types in and around Amboli Ghat. The finding of this study can provide
baseline data for intensive studies in the future. The study also highlights the ecological
significance of this highly biodiverse spot in the
Western Ghats of India.
Methods
Study area
An area of
around 54km2 covering locations like Amboli
Town, Papdi, Malai, Chaukul, Mahadevgarh, Parpoli, and adjoining areas (Fig. 1), was explored for the
study since each zone varies in its landscape type. In addition to the slope of the valley of Amboli Ghat, this study also
included areas of lower hilly terrains, as the valley is surrounded by hills on
almost all sides. The present study
explores areas used for agriculture and human settlements as well as natural
habitats such as forest patches, grasslands, streambanks,
and scrublands. Locations around the
collection of large wetlands near Papdi were also
investigated. Habitat details of the
above-mentioned locations are as follows:
1) Papdi (15.8880N & 74.03720E) – a
mostly flat terrain with a slightly undulating land, agricultural fields, and
streams present with temporary marshes during monsoon and early winter.
2) Malai Forest
(15.9410N & 74.0010E)
- dense evergreen forest.
3) Chaukul Road (15.9430N & 74.0310E) – a flat
terrain covered with vegetation during monsoon and dry scrub in late winter and
summer.
4) Amboli Town (15.9660N & 74.0040E)
- human settlements near Amboli reserve forest.
5)
Mahadevgarh Road (15.9670N & 73.9900E)
- evergreen forest cover with sporadic open grassland patches.
6) Amboli Ghat (15.9340N & 73.9900E) - steep
escarpments with moist deciduous and evergreen forests.
7) Parpoli (15.9500N & 73.9750E) - foothills of Amboli receiving maximum rainfall in the study area. The short grown vegetation remains submerged
under water till early winter. The remaining area is covered by evergreen forests.
Bimonthly
surveys were carried out in the selected areas of various habitats from March
2009 to March 2012. The areas were
surveyed using binoculars and digital cameras for documenting bird species. Direct observations and
noting of species sighted were made by walking on the roads and village tracks
and through grasslands and agriculture areas. Monitoring of areas was done in the morning
from 6:00 to 10:00 hr as well as in the evening from
15:00 to 19:00 hr. Visits were also made in the afternoons and late evenings to
check the activities of the avian fauna at different times. Birds were identified using widely accepted
field guides like Ali & Ripley (1983) and Grimmett
et al. (1998,2011). For taxonomy, species
sequence, and nomenclature, we followed Praveen et al. (2016).
The status of
birds was assigned based on the following criteria:
1) Resident -
if a bird was seen all throughout the year (not necessarily nesting).
2) Winter
visitor - if a bird was seen only during the period from December to February.
3) Summer
visitor - if a bird was seen only during the period from March to May.
The birds were
assigned strictly with reference to the study area on the basis of presence or
absence method. The birds that showed
irregular trends of sighting and population fluctuations (non-seasonal) were
placed under uncertain status. Current
status of threatened categories was adopted from IUCN Red list (IUCN 2016).

Results
A total of 208
species was recorded during the study (Table 1), constituting around 15% of the
total species listed in the Indian subcontinent by Grimmett
et al. (2011). Birds from 64 families
were recorded. Family-wise analysis
showed that the families Accipitridae and Muscicapidae (14 species each) followed by Ardeidae (10 species) dominated the avian fauna, indicating
a healthy bird diversity in the region. Out of the total species encountered,
analysis of data revealed that 165 species were residents, 38 species were
winter visitors, two species were summer visitors, and the remaining species
have an uncertain status. The status of
three species, European Roller Coracias garrulus, Asian Pied Starling Gracupica
contra, and Green Avadavat Amandava formosa, was considered
uncertain as they showed irregular trends of sighting and population
fluctuations (non-seasonal). Since there
are no habitats appropriate for Green Avadavat in the study area, the
individuals sighted could be those escaped from cages.A comparative graph was prepared to see the
differences in avian faunal diversity in the locations in the study area which
revealed Parpoli region with maximum number of
species (181 species of birds) (Figs. 2 & 3). A few bird species like
Pompadour Green Pigeon Treron pompadora, Grey-bellied Cuckoo Cacomantis
passerinus, Drongo
Cuckoo Surniculus lugubris,
Blue-faced Malkoha Phaenicophaeus
viridirostris, Lesser Golden-backed Woodpecker Dinopium benghalense,
Yellow-fronted Pied Woodpecker Dendrocopos mahrattensis, White-naped
Woodpecker Chrysocolaptes festivus, Heart-spotted Woodpecker Hemicircus
canente and Little Spiderhunter
Arachnothera longirostra
(Table 1) were sighted only at the low-lying well-wooded region of Parpoli in the study area.
Studies show that habitats with structurally complex matrices have
greater potential for supporting the populations of forest birds than open
areas such as pastures (Raman 2006).
Sixty-one species of birds are recognized as endemic to India (Praveen
et al. 2016), of which 13 were sighted in the study area. A few birds that showed
local seasonal migration due to heavy rainfall in the higher altitude areas of Amboli.
Based on the
present study, it can be concluded that there are 11 species of birds in the
study area that are struggling for their existence throughout their
distributional range and therefore can be placed under threat categories as
identified by IUCN (2016). These species
are the Vulnerable Woolly-necked Stork Ciconia
episcopus, Nilgiri Wood
Pigeon Columba elphinstonii (observed
roosting), and Green Avadavat (observed roosting) and the Near Threatened
Black-necked Stork Ephippiorhynchus asiaticus, Black-headed Ibis Threskiornis
melanocephalus, Oriental Darter Anhinga
melanogaster, Pallid Harrier Circus macrourus,
River Tern Sterna aurantia, Great Hornbill Buceros bicornis,
Malabar Pied Hornbill Anthracoceros coronatus, and Grey-headed Bulbul Brachypodius
priocephalus (observed feeding and
roosting). Of these, Grey-headed Bulbul
and Nilgiri Wood Pigeon are endemic to the Western
Ghats. Vultures were not encountered in
the present study.

Table 1. A systematic checklist of bird
species of Amboli Ghat,
Maharashtra State, India
|
|
Family |
Scientific name |
Common name |
Status |
Sighting location |
|
1 |
Anatidae |
Anas poecilorhynca |
Indian Spot-billed Duck |
R |
AR |
|
2 |
Phasianidae |
Pavo cristatus |
Indian Peafowl |
R |
AR |
|
3 |
|
Perdicula asiatica |
Jungle Bush Quail |
R |
AR |
|
4 |
|
Gallus sonneratii |
Grey Junglefowl |
R, EI |
AR |
|
5 |
|
Galloperdix spadicea |
Red Spurfowl |
R, EI |
AR |
|
6 |
Podicipedidae |
Tachybaptus ruficollis |
Little Grebe |
R |
PP |
|
7 |
Columbidae |
Columba livia |
Rock Pigeon |
R |
AR |
|
8 |
|
C. elphinstonii |
Nilgiri Wood Pigeon |
R, EI |
AT |
|
9 |
|
Streptopelia orientalis |
Oriental Turtle Dove |
R |
AR |
|
10 |
|
S. chinensis |
Spotted Dove |
R |
AR |
|
11 |
|
Treron pompadora |
Pompadour Green Pigeon |
R |
PR |
|
12 |
|
T. phoenicoptera |
Yellow-legged Green Pigeon |
R |
AR |
|
13 |
|
Chalcophaps indica |
Emerald Dove |
R |
AR |
|
14 |
Podargidae |
Batrachostomus moniliger |
Sri Lankan Frogmouth |
R |
CR, ML, MG |
|
15 |
Caprimulgidae |
Caprimulgus indicus |
Grey Nightjar |
R |
AR |
|
16 |
|
C. atripennis |
Jerdon’s Nightjar |
R |
CR |
|
17 |
|
C. affinis |
Savanna Nightjar |
R |
AT, CR |
|
18 |
Apodidae |
Hemiprocne coronata |
Crested Treeswift |
R |
PR |
|
19 |
|
Apus pacificus |
Fork-tailed Swift |
W |
AR |
|
20 |
|
A. affinis |
Indian House Swift |
R |
AR |
|
21 |
Cuculidae |
Centropus sinensis |
Greater Coucal |
R |
AR |
|
22 |
|
Phaenicophaeus viridirostris |
Blue-faced Malkoha |
R |
PR |
|
23 |
|
Clamator jacobinus |
Pied Cuckoo |
S |
AR |
|
24 |
|
Eudynamys scolopaceus |
Asian Koel |
R |
AR |
|
25 |
|
Cacomantis passerinus |
Grey-bellied Cuckoo |
R |
PR |
|
26 |
|
Surniculus lugubris |
Drongo Cuckoo |
R |
PR |
|
27 |
|
Hierococcyx varius |
Common Hawk Cuckoo |
R |
AR |
|
28 |
|
Cuculus canorus |
Eurasian Cuckoo |
W |
AR |
|
29 |
Rallidae |
Rallina eurizonoides |
Slaty-legged Crake |
R |
CR |
|
30 |
|
Zapornia pusilla |
Ballion’s Crake |
W |
PP |
|
31 |
|
Amaurornis phoenicurus |
White-breasted Waterhen |
R |
AR |
|
32 |
Ciconiidae |
Ciconia episcopus |
Woolly-necked Stork |
R |
PP |
|
33 |
|
Ephippiorhynchus asiaticus |
Black-necked Stork |
R |
PP |
|
34 |
Ardeidae |
Ixobrychus cinnamoneus |
Cinnamon Bittern |
R |
PP, AT |
|
35 |
|
Nycticorax nycticorax |
Black-crowned Night Heron |
R |
AR |
|
36 |
|
Butorides striata |
Striated Heron |
R |
PP |
|
37 |
|
Ardeola grayii |
Indian Pond Heron |
R |
AR |
|
38 |
|
Bubulcus ibis |
Cattle Egret |
R |
AR |
|
39 |
|
Ardea cinerea |
Grey Heron |
W |
PP, AT |
|
40 |
|
A. purpurea |
Purple Heron |
R |
PP |
|
41 |
|
A. alba |
Greater Egret |
R |
AR |
|
42 |
|
A. intermedia |
Median Egret |
R |
AR |
|
43 |
|
Egretta garzetta |
Little Egret |
R |
AR |
|
44 |
Threskiornithidae |
Threskiornis melanocephalus |
Black-headed Ibis |
R |
PP |
|
45 |
Phalacrocoracidae |
Microcarbo niger |
Little Cormorant |
R |
AR |
|
46 |
Anhingidae |
Anhinga melanogaster |
Oriental Darter |
R |
PP |
|
47 |
Charadriidae |
Vanellus malabaricus |
Yellow-wattled
Lapwing |
W |
AT |
|
48 |
|
V. indicus |
Red-wattled
Lapwing |
R |
AR |
|
49 |
Scolopacidae |
Actitis hypoleucos |
Common Sandpiper |
W |
AR |
|
50 |
|
Tringa totanus |
Common Redshank |
W |
PP |
|
51 |
|
T. glareola |
Wood Sandpiper |
W |
AR |
|
52 |
Turnicidae |
Turnix suscitator |
Barred Buttonquail |
R |
AR |
|
53 |
Laridae |
Sterna aurantia |
River Tern |
R |
AR |
|
54 |
Accipitridae |
Elanus caeruleus |
Black-winged Kite |
R |
AR |
|
55 |
|
Pernis ptilorhynchus |
Oriental Honey Buzzard |
R |
AR |
|
56 |
|
Spilornis cheela |
Crested Serpent Eagle |
R |
AR |
|
57 |
|
Circaetus gallicus |
Short-toed Snake Eagle |
R |
AR |
|
58 |
|
Ictinaetus malaiensis |
Black Eagle |
R |
AR |
|
59 |
|
Aquila rapax |
Tawny Eagle |
R |
AT |
|
60 |
|
A. fasciata |
Bonelli’s Eagle |
R |
AR |
|
61 |
|
Hieraaetus pennatus |
Booted Eagle |
W |
AR |
|
62 |
|
Circus macrourus |
Pallid Harrier |
W |
AR |
|
63 |
|
C. pygargus |
Montagu’s Harrier |
W |
CR, PP |
|
64 |
|
Accipiter badius |
Shikra |
R |
AR |
|
65 |
|
Haliastur indus |
Brahminy Kite |
R |
AR |
|
66 |
|
Milvus migrans |
Black Kite |
R |
AR |
|
67 |
|
Butastur teesa |
White-eyed Buzzard |
R |
AR |
|
68 |
Tytonidae |
Tyto alba |
Common Barn Owl |
R |
AR |
|
69 |
Strigidae |
Athene brama |
Spotted Owlet |
R |
AR |
|
70 |
|
Strix leptogrammica |
Brown Wood Owl |
R |
AR |
|
71 |
|
Bubo bengalensis |
Indian Eagle Owl |
R |
AR |
|
72 |
|
Ketupa zeylonensis |
Brown Fish Owl |
R |
AR |
|
73 |
Bucerotidae |
Buceros bicornis |
Great Hornbill |
R |
AR |
|
74 |
|
Anthracoceros coronatus |
Malabar Pied Hornbill |
R |
AR |
|
75 |
|
Ocyceros griseus |
Malabar Grey Hornbill |
R, EI |
AR |
|
76 |
|
O. birostris |
Indian Grey Hornbill |
R |
AR |
|
77 |
Upupidae |
Upupa epops |
Common Hoopoe |
R |
AR |
|
78 |
Picidae |
Picumnus innominatus |
Speckled Piculet |
R |
ML |
|
79 |
|
Hemicircus canente |
Heart-spotted Woodpecker |
R |
PR |
|
80 |
|
Dinopium benghalense |
Lesser Golden-backed Woodpecker |
R |
PR, ML |
|
81 |
|
Micropternus brachyurus |
Rufous Woodpecker |
R |
PR |
|
82 |
|
Chrysocolaptes festivus |
White-naped
Woodpecker |
R |
PR |
|
83 |
|
Dendrocopos mahrattensis |
Yellow-fronted Pied Woodpecker |
R |
PR |
|
84 |
Ramphastidae |
Psilopogon zeylanica |
Brown-headed Barbet |
R |
PR |
|
85 |
|
P. viridis |
White-cheeked Barbet |
R, EI |
AR |
|
86 |
Meropidae |
Merops orientalis |
Green Bee-eater |
R |
AR |
|
87 |
|
M. leschenaulti |
Chestnut-headed Bee-eater |
R |
AR |
|
88 |
Coraciidae |
Coracias benghalensis |
Indian Roller |
R |
AR |
|
89 |
|
C. garrulus |
European Roller |
UC |
CR |
|
90 |
Alcedinidae |
Ceyx erithaca |
Oriental Dwarf Kingfisher |
R |
AT, CR, ML |
|
91 |
|
Alcedo meninting |
Blue-eared Kingfisher |
R |
PR, AT |
|
92 |
|
A. atthis |
Common Kingfisher |
R |
AR |
|
93 |
|
Ceryle rudis |
Pied Kingfisher |
R |
AR |
|
94 |
|
Pelargopis capensis |
Stork-billed Kingfisher |
R |
AR |
|
95 |
|
Halcyon smyrnensis |
White-throated Kingfisher |
R |
AR |
|
96 |
|
H. pileata |
Black-capped Kingfisher |
R |
PP |
|
97 |
Falconidae |
Falco tinnunculus |
Common Kestrel |
W |
AR |
|
98 |
|
F. peregrinus |
Peregrine Falcon |
R |
AR |
|
99 |
Psittaculidae |
Psittacula cyanocephala |
Plum-headed Parakeet |
R |
AR |
|
100 |
|
P. krameri |
Rose-ringed Parakeet |
R |
AR |
|
101 |
|
Loriculus vernalis |
Vernal Hanging Parrot |
R |
AR |
|
102 |
Pittidae |
Pitta brachyura |
Indian Pitta |
W |
AR |
|
103 |
Campephagidae |
Pericrocotus cinnamomeus |
Small Minivet |
R |
PR |
|
104 |
|
P. flammeus |
Scarlet Minivet |
R |
AR |
|
105 |
|
Lalage melanoptera |
Black-headed Cuckooshrike |
R |
PR |
|
106 |
Oriolidae |
Oriolus xanthornus |
Black-hooded Oriole |
R |
PR |
|
107 |
|
O. kundoo |
Indian Golden Oriole |
W |
AR |
|
108 |
Artamidae |
Artamus fuscus |
Ashy Woodswallow |
R |
PR |
|
109 |
Vangidae |
Hemipus picatus |
Bar-winged Flycatcher Shrike |
R |
PR |
|
110 |
|
Tephrodornis virgatus |
Large Woodshrike |
R |
MG, PR |
|
111 |
|
T. pondicerianus |
Common Woodshrike |
R |
PR |
|
112 |
Aegithinidae |
Aegithina tiphia |
Common Iora |
R |
AR |
|
113 |
Dicruridae |
Dicrurus macrocercus |
Black Drongo |
R |
AR |
|
114 |
|
D. leucophaeus |
Ashy Drongo |
R |
AR |
|
115 |
|
D. caerulescens |
White-bellied Drongo |
R |
PR |
|
116 |
|
D. paradiseus |
Greater Racket-tailed Drongo |
R |
PR |
|
117 |
Rhipiduridae |
Rhipidura aureola |
White-browed Fantail |
R |
PR |
|
118 |
|
R. albicollis |
White-throated Fantail |
R |
PR |
|
119 |
Laniidae |
Lanius schach |
Long-tailed Shrike |
R |
AR |
|
120 |
|
L. vittatus |
Bay-backed Shrike |
R |
AR |
|
121 |
Corvidae |
Dendrocitta vagabunda |
Rufous Treepie |
R |
PR |
|
122 |
|
Corvus splendens |
House Crow |
R |
AR |
|
123 |
|
C. macrorhynchos |
Large-billed Crow |
R |
AR |
|
124 |
Monarchidae |
Hypothymis azurea |
Black-naped
Monarch |
R |
AR |
|
125 |
|
Terpsiphone paradisi |
Indian Paradise-flycatcher |
R |
AR |
|
126 |
Dicaeidae |
Dicaeum agile |
Thick-billed Flowerpecker |
R |
AR |
|
127 |
|
D. erythrorhynchos |
Pale-billed Flowerpecker |
R |
AR |
|
128 |
|
D. concolor |
Plain Flowerpecker |
R |
AR |
|
129 |
Nectariniidae |
Arachnothera longirostra |
Little Spiderhunter |
R |
PR |
|
130 |
|
Leptocoma zeylonica |
Purple-rumped
Sunbird |
R |
AR |
|
131 |
|
L. minima |
Crimson-backed Sunbird |
R, EI |
AR |
|
132 |
|
Cinnyris asiaticus |
Purple Sunbird |
R |
AR |
|
133 |
|
Aethopyga vigorsii |
Vigors’s Sunbird |
R, EI |
AR |
|
134 |
Irenidae |
Irena puella |
Asian Fairy Bluebird |
R |
PR |
|
135 |
|
Chloropsis aurifrons |
Golden-fronted Leafbird |
R |
AR |
|
136 |
Ploceidae |
Ploceus philippinus |
Baya Weaver |
R |
AR |
|
137 |
Estrildidae |
Amandava formosa |
Green Avadavat* |
UC, EI |
AT |
|
138 |
|
Euodice malabarica |
Indian Silverbill |
R |
PR |
|
139 |
|
Lonchura striata |
White-rumped Munia |
R |
AR |
|
140 |
|
L. punctulata |
Scaly-breasted Munia |
R |
AR |
|
141 |
|
L. malacca |
Black-headed Munia |
R |
AR |
|
142 |
Passeridae |
Passer domesticus |
House Sparrow |
R |
AR |
|
143 |
|
Gymnoris xanthocollis |
Yellow-throated Sparrow |
R |
PR |
|
144 |
Motacillidae |
Dendronanthus indicus |
Forest Wagtail |
W |
ML, MG, CR |
|
145 |
|
Anthus rufulus |
Paddyfield Pipit |
R |
AR |
|
146 |
|
Motacilla cinerea |
Grey Wagtail |
W |
AR |
|
147 |
|
M. citreola |
Citrine Wagtail |
W |
AR |
|
148 |
|
M. maderaspatensis |
White-browed Wagtail |
W |
AR |
|
149 |
|
M. alba |
White Wagtail |
W |
AR |
|
150 |
Fringillidae |
Erythrina erythrina |
Common Rosefinch |
W |
AR |
|
151 |
Paridae |
Parus cinereus |
Cinereous Tit |
R |
PR |
|
152 |
|
P. xanthogenys |
Black-lored
Tit |
R |
AR |
|
153 |
Alaudidae |
Galerida malabarica |
Malabar Lark |
R, EI |
AR |
|
154 |
Cisticolidae |
Prinia hodgsonii |
Grey-breasted Prinia |
R |
PR |
|
155 |
|
P. socialis |
Ashy Prinia |
R |
AR |
|
156 |
|
P. inornata |
Plain Prinia |
R |
AR |
|
157 |
|
Orthotomus sutorius |
Common Tailorbird |
R |
AR |
|
158 |
Acrocephalidae |
Acrocephalus dumetorum |
Blyth's Reed Warbler |
W |
AR |
|
159 |
|
A. agricola |
Paddyfield Warbler |
W |
AR |
|
160 |
Hirundinidae |
Cecropis daurica |
Red-rumped
Swallow |
R |
AR |
|
161 |
|
Hirundo smithii |
Wire-tailed Swallow |
R |
AR |
|
162 |
|
H. rustica |
Barn Swallow |
R |
AR |
|
163 |
|
Ptyonoprogne concolor |
Dusky Crag Martin |
R |
AR |
|
164 |
Pycnonotidae |
Hypsipetes leucocephalus |
Black Bulbul |
R |
AR |
|
165 |
|
Pycnonotus melanicterus |
Flame-throated Bulbul |
R |
PR, GT |
|
166 |
|
P. jocosus |
Red-whiskered Bulbul |
R |
AR |
|
167 |
|
P. cafer |
Red-vented Bulbul |
R |
AR |
|
168 |
|
Brachypodius priocephalus |
Grey-headed Bulbul |
R, EI |
AR |
|
169 |
|
Acritillas indica |
Yellow-browed Bulbul |
R |
AR |
|
170 |
Phylloscopidae |
Phylloscopus collybita |
Common Chiffchaff |
W |
AR |
|
171 |
|
P. tytleri |
Tytler’s Leaf Warbler |
W |
PR |
|
172 |
|
P. affinis |
Tickell's Leaf Warbler |
W |
PR, ML |
|
173 |
|
Seicercus nitidus |
Green Leaf Warbler |
W |
AR |
|
174 |
|
S. trochiloides |
Greenish Leaf Warbler |
W |
AR |
|
175 |
Sylviidae |
Curruca crassirostris |
Eastern Orphean
Warbler |
W |
PR |
|
176 |
|
C. curruca |
Lesser Whitethroat |
W |
PR |
|
177 |
|
Chrysomma sinense |
Yellow-eyed Babbler |
R |
PR |
|
178 |
Zosteropidae |
Zosterops palpebrosus |
Oriental White-eye |
R |
PR |
|
179 |
Timaliidae |
Pomatorhinus horsfieldii |
Indian Scimitar Babbler |
R |
AR |
|
180 |
|
Dumetia hyperythra |
Tawny-bellied Babbler |
R |
AR |
|
181 |
|
Rhopocichla atriceps |
Dark-fronted Babbler |
R |
PR |
|
182 |
Pellorneidae |
Pellorneum ruficeps |
Puff-throated Babbler |
R |
AR |
|
183 |
Leiothrichidae |
Alcippe poioicephala |
Quaker Tit Babbler |
R |
AR |
|
184 |
|
Argya malcolmi |
Large Grey Babbler |
R |
AT |
|
185 |
|
A. subrufa |
Rufous Babbler |
R, EI |
AR |
|
186 |
|
Turdoides striata |
Jungle Babbler |
R |
AR |
|
187 |
Sturnidae |
Pastor roseus |
Rosy Starling |
W |
AR |
|
188 |
|
Gracupica contra |
Asian Pied Starling |
UC |
AR |
|
189 |
|
Sturnia pagodarum |
Brahminy Starling |
R |
AR |
|
190 |
|
Acridotheres tristis |
Common Myna |
R |
AR |
|
191 |
|
A. fuscus |
Jungle Myna |
R |
AR |
|
192 |
|
Gracula religiosa |
Hill Myna |
R |
AR |
|
193 |
Muscicapidae |
Copsychus saularis |
Oriental Magpie Robin |
R |
AR |
|
194 |
|
Kittacincla malabaricus |
White-rumped Shama |
R |
AR |
|
195 |
|
Muscicapa dauurica |
Asian Brown Flycatcher |
W |
AR |
|
196 |
|
Cyornis pallidipes |
White-bellied Blue Flycatcher |
R, EI |
CR, ML, PR, MG |
|
197 |
|
C. tickelliae |
Tickell’s Blue Flycatcher |
R |
AR |
|
198 |
|
C. rubeculoides |
Blue-throated Flycatcher |
W |
MG |
|
199 |
|
Eumyias thalassinus |
Verditer Flycatcher |
W |
AR |
|
200 |
|
Larvivora brunnea |
Indian Blue Robin |
W |
AR |
|
201 |
|
Myophonus horsfieldii |
Malabar Whistling Thrush |
R, EI |
AR |
|
202 |
|
Ficedula parva |
Red-breasted Flycatcher |
W |
ML, PR |
|
203 |
|
Monticola cinclorhynchus |
Blue-capped Rock Thrush |
W |
ML, PR |
|
204 |
|
M. solitarius |
Blue Rock Thrush |
W |
AR |
|
205 |
|
Saxicola maurus |
Siberian Stonechat |
W |
CR, PR |
|
206 |
|
S. caprata |
Pied Bushchat |
R |
AR |
|
207 |
Turdidae |
Geokichla citrina |
Orange-headed Thrush |
R |
AR |
|
208 |
|
Turdus simillimus |
Indian Blackbird |
S |
AR |
EI - endemic to India (from Praveen et al. 2016), * - sighted once.
Abbreviations for location: PR - Parpoli region, GT - Ghat region, AT - Amboli Town, CR - Chaukul Road, ML - Malai region, PP - Papdi region, MG - Mahadevgarh region, AR - all regions
Discussion
A list with
authentic records reflects the true natural diversity of the avian fauna of any
region. For taxa that are widespread or
migrating, records in such lists form an essential part of the information that
can be used to map their global distribution and seasonal movements. The Amboli Ghat area still provides some potential habitats for the
declining population of many bird species.
During the breeding season, Grey-headed Bulbuls were observed foraging
in areas of Amboli Ghat
dominated by sub-canopy trees bearing fruits.
Fruit availability is also an important factor that decides the breeding
season of this species (Balakrishnan 2011). The occurrence of Malabar Grey Hornbill can
be attributed to the retention of fruits in the canopy, which provides food for
the species (Raman & Mudappa 2003). Open areas are of utmost importance for bird
populations as these areas provide better visibility for vigilance against
predators and free movement for food procurement (Desai & Shanbhag 2012). It
is the need of the hour to monitor these areas systematically in the rapidly changing
environment with a focused study on the status, distribution, and conservation
of the avian fauna of the region, which can be achieved only through
strengthening public participation species.
One of the
problems faced by Amboli Ghat
in the recent years is the disturbance caused by humans along with
deforestation for plantation, development, and mining. Changes in vegetation components could affect
the availability of food resources and microclimatic conditions, which could
then affect the richness and abundance of bird species (Johns 1991).
Animals in
protected areas may face interference in their daily activities due to tourists
and their associated activities. Tourism
in protected areas can have negative influences on animal populations, as tourists
often seek out rare or spectacular species during sensitive times such as
breeding or nesting (Knight & Cole 1995).
Where human traffic is frequent, species withdraw, change behaviour, or become habituated to human presence
(Griffiths & van Schaik 1993). During the current study, Blue-capped Rock
Thrush Monticola cinclorhynchus,
Yellow-browed Bulbul Acritillas indica, and Quaker Tit Babbler Alcippe
poioicephala were found feeding on garbage left
by tourists.
Amboli Ghat is visited
extensively by tourists and most
of the tourist activities are concentrated around the Amboli
Waterfall on State Highway 121 on the outskirts of Amboli
Town. Good connectivity by roads to
Karnataka, Goa, and the rest of Maharashtra State results in about 15,000
tourists visiting Amboli during weekends between July
and September. During this period, the
roadsides are littered without care.
During the study period, it was revealed that around 20,000 vehicles pass
through the study area, mainly Amboli Town on State
Highway 121, which results in a number of roadkills
and affects the feeding and nesting of birds.
It was found that species like Oriental Dwarf
Kingfisher Ceyx erithaca
at Amboli are vehemently sought after by
photographers and their enthusiasm has disturbed some of their favourite nesting sites.
There are three main motorable roads in Amboli Ghat area. During monsoon, an average of around 24 roadkills of animals, mainly composing of reptiles and
amphibians, are recorded per day. Most
of these reptile and amphibian species were from the Endangered category of the
IUCN Red Data Book (IUCN 2016) and were observed on all the motorable
roads each day during the study period.
The strategy of biodiversity conservation is based on applying methods
of protection in a specified area.
Tourism development must be carefully managed to avoid turning Amboli Ghat into yet another
tourist town where bottles, wrappers, plastics, and billboards dominate the
landscape. Though ecotourism is capable
of generating high revenue for natural areas that need protection, planning and
development of infrastructure pertaining to tourism, its marketing should focus
on conservation of nature, minimizing negative visitor impact, and involvement
and employment of local populations in all aspects of business operations. Commercialization programs should have
policies to meet higher social and environmental goals like building ecolodges powered by alternative energy resources and
allowing travellers to stay in relative comfort while having magnificent
wildlife-viewing from their doorsteps, which minimally impacts the local
environment.
The following
management strategies can be implemented at Amboli Ghat (Wood 2002):
1) Provide
adequate budget to conserve popular tourist areas and earmark tourism fees for
conservation.
2) Tourism
businesses should pay impact fees that should fund infrastructure for solid
waste treatment, sewage treatment, electricity, water
and tourists must receive clear incentives for conserving water and
electricity.
3)
Environmental impact monitoring programs should be regularly implemented.
4)
Well-managed trails and camping areas should be clearly marked with rules for
low-impact use.
5)
Restrictions should be in place for the type of vehicles permitted in specific zones,
speed limits, dumping of waste, and off-road driving.
6) Training
programs should be initiated at local levels to provide local inhabitants with
the opportunity to run their own businesses.
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