International
Journal of Zoology and Applied Biosciences |
ISSN: 2455-9571 |
|
Volume 3, Issue 2, pp: 426-439, 2018 |
|
|
Research Article |
|
|
|
|
|
Avifaunal
diversity of Anantapuramu
(semi-arid) District, Andhra Pradesh, India
V.V. Bala Subramanyam* Department of
Zoology, Sri Krishnadevaraya University, Anantapuramu, Andhra Pradesh, India |
|
|
Article History: Received 26th
January 2018; Accepted 31st March 2018; Published 5th
June 2018 |
|
|
The
present study was undertaken as a part to update and document the available
bird species from Anantapuramu district in Andhra Pradesh, India. A total of
124 bird species belonging to the 52 families with Accipitridids as the most
dominant family, while insectivorous
(55 species), followed by carnivorous (26 species), granivore (10 species),
Omnivorous (3) and Frugivore (2 species). By studying the diversity of
birds in Anantapuramu district, this study is intended to facilitate a
further investigation of these avian fauna in dry land regions like
Anantapuramu district, in terms of their contribution to ecosystem services. |
|
Introduction
Indian sub-continent is declared as
one of the twelve mega diversity countries of the world (Sinha et al., 2010) with two biodiversity hot
spots, the Himalaya and the Western Ghats of a total of 35 such sites
identified throughout the globe (ENVIS Online 2016). Around 1.2 million species
of plants, animals and micro-organisms have been reported so far from India of
which, the animal species constitute 7.28 per cent of the total world animal
species. Zoologists are of the view that 4, 00,000 species are yet to be
explored and identified, a majority of which are expected to be micro-organisms
and invertebrates (MoEF and Kalpavriksh, 2004).
The Indian sub-continent possesses a
rich avian diversity and is home to 1,300 species of birds (Grimmettet et al., 2000). Ornithological studies
have been conducted in Andhra Pradesh which includes Ali’s (1933–34), Abdulali
(1945) and Ripley et al. (1987–88), etc. The recent works carried out
on avifauna of united Andhra Pradesh by earlier workers such as Anand (2000),
Srinivasulu (2004), Kannan et al. (2008), David et al. (2011), Narayana et al. (2013) and Prasad et al. (2014) and
Subramanyam et al. (2016); Subramanyam (2017a). Revised
documented information on the current status of avian fauna does not exist
other than above mentioned studies.
Knowledge about the status and
threats to dry land biodiversity of this region is limited. Many species of dry
land are under threat of extinction due to natural causes or anthropogenic
activities. Therefore, it is essential to prepare and document a checklist of avian species found
in the entire Anantapuramu district. It is the largest district in Andhra
Pradesh covering a vast area of 19,130 square kmsand the 7th largest
district in India (Srivastava,
Dayawanti et
al. (2010). It is an attempt to provide up-to-date documented
information of avifauna and their habitat utilization pattern, as part of broader
baseline information for future conservation programmes. This study further
facilities wider scope of understanding avian diversity in semi-arid region of Anantapuramu
district in terms of their contribution to ecosystem services.
Material and Methods
Study
area
Anantapuramu district lies between
13'-40' and 15'-15 Northern Latitude and 76'-50' and 78'-30' Eastern Longitude
(Figure 1). The District may be divided
into 3 Natural divisions i.e., Northern zone with 12 mandalscomprising larger
areas of black cotton soils; Central division with 15 mandals which are mainly
made up of arid Treeless, expanse of poor Red Soils; and High Level terrain of
the district circles with 4 mandals connected to Mysore plateau at a higher
elevation of the
rest of the
District (Table 1) (Subramanyam and Khan 2017). This part has average sandy red
soils of normal productivity. This region experiences extremes of weather
conditions with maximum temperatures
fluctuating from 39 to 43°C. Further, the geographical location of Anantapuramu
district is such that it does not get the full
benefit of either of the monsoons. The
district falls under the rain shadow area with the normal rainfall being 553 mm.
Dry land farming (arid agro-ecosystem) is the major agricultural practice
noticed in the surrounding landscapes of the study area. Bengal gram, groundnut and paddy are the
major crops grown.
Figure 1. Location map of Anantapuramu District.
Table 1. Natural geographical divisions of
Anantapuramu district.
|
Northern region mandals (NRM) |
Central region mandals (CRM) |
High level Land mandals (HLM) |
|
Rayadurg, Kanekal, Beluguppa, Gooty, Guntakal,Vajrakarur,
Uravakonda, Vidapanakal, Yadiki, Tadipatri, Putlur and Yellannur containing
larger areas of Black Cotton soils. |
Kalyandurg,
Kambadur, Settur, Brahmasamudram, Ramagiri, Kanaganapalli, C.K. Palli,
Dharmavaram, Bathalapalli, Tadimarri, Mudigubba, Anantapuramu, Kudair, Pamidi
and Peddavadugur which are mainly made up of arid, expanse of poor Red Soils. |
Penukonda,
Roddam, Gudibanda and Agali which connect with Mysore plateau at a higher
elevation of the rest of the District. This part has average sandy red soils
of normal productivity. |
Vegetation cover of
Anantapuramu district: According to Champion and Seth (1968) classified these forests as 6A/C1
Southern Tropical Thorn Forests, which is thin
and scanty andthis type of forest is found within almost all drier parts
of Andhra Pradesh. The main floral species in this forest include Acacia chundra, Albizla amara, Balanites aegyptiaca,
Anisochilus carnosus, Canthium parviflorum, Erythroxylon monogynum, Fiacourtia indica,
Prernna tomentosa, Ziziphus spp., Podonaea viscosa, Euphorbia antiquorum, Dichrostachis
cinera, Capparisore vispina, Maytenus, Carissa spinarum, Grewia tenax, Albizzia
amara, Chloroxylon sweitenia, Feronia limonia, Canthium didynium, Wrightia tinctoria,
Cassia fistula, Bauhinia rasimosa, Acacia
arabica, Acacia sundra, Dichrostachis cinerea, Dolichendron falcata, Cassia
carandus, Randia dumetorum,
Gymnosporia montana, Gmelina asiatica, Zizyphus numularia, Ixora arborea,
Cadaba fruiticosa, Cassia auriculata., Euphorbia antiquorum, Acacia ferruginea, Acacia planifrons, Acacia
torta, Acacia horrida, Ziziphus glabrata, Scutia
myrtina, Rhus mysurensis, Canthium coromandelianum, Capparisssp, Sennaalex andrina, Grasses include Sympopogan collaratus, Heteropogan contortus,
Panicum repens, Cynodon dactylone, etc. (Pullaiah and Yesoda 1989; Subramanyam 2017 b).
Methodology
We have conducted an Extensive
Avian Survey for revised documented information on current status of avian
fauna in the study area for one year, from August 2015 to September 2017 by
employing the following standard methods. 1) Line-transect method; and 2) Point
count method. Line-transect method:
Underthis
method, a straight line of one km is drawn, and all birds heard or seen up
to a range of 25 m on either side of the transect are recorded. Point count method: Underthis method, the
observer will stand at in a haphazardly chosen point
and
record bird species
seen and heard overa 50 m radius for 5 minutes. This observation run is conducted/
repeated atanother point at least 300 m from the first point. In addition to
this, opportunistic bird sightings were recordedwhile travelling within the study
region (Emlen, 1974; Sutherlad, 2006;
Rajashekara, 2015 and Nautiyal 2015) and observations were made twice a
day when avifauna is usually most active (05:00 am to 10 am and evening 03:00
pm to 06:00 pm). Birds were observed with the help of an Olympus Binocular
(8X42) and photographs taken using a Canon EOS 700D SLR camera. Sometimes, birds
were identified on the basis of their calls. Identification of birds was done
by using standard field guides (Ali
et al., 1983; Manakadan, 2011 and Arlott,
2014).
The
first survey was conducted inthe central region of the district covering 16
mandals, while a subsequent survey run was carried out in the northern region of
the district comprising12 mandals and the finalsurvey was carried out in the
high level terrain consisting of 4 mandals in avian distribution were also recorded
across the three regions.
Results
A
total of 124 bird species belonging to the 52 families were recorded acrossvarious
landscapes of the study area (Table 2).
Accipitridae was found to be the most dominant family consistingof 16
species in the study area, followed by Muscicapidae (7 species), Motacillidae
(6 species), Cisticolidae and Cuculidae (each five species), Alaudidae and Columbidae
(each four species) (Figure 2). The maximum number of bird species belong to Onlyinsectivorous (55 species), followed by
carnivores (26 species), granivore (10 species), Omnivores (threespecies) and
Frugivore (two species) (Table 3). The habitat details of all bird speciesrecorded
from study area are given in Table 2.
Figure 2. Avian faunal diversity among various
families in Anantapuramu district.
Table 2. Check list of Avifauna along with their feeding habits
and habitat types and conservation status in the study area.
|
S.No. |
Scientific
name |
Common
Name |
Feeding
Habit |
Location
of the district |
Type of
habitat |
IUCN
Status |
|
|
Family: Accipitridae |
|||||||
|
1 |
Accipiter badius |
Shikra |
C |
NRM |
Found in dry areas with trees. |
LC |
|
|
2 |
Accipiter nisus |
Eurasian Sparrow Hawk |
C |
CRM |
Inhabits a wide variety of forest types. |
LC |
|
|
3 |
Aquila rapax |
Tawny Eagle |
C |
CRM |
Semi-desert and arid; only absent from forest |
LC |
|
|
4 |
Circaetus gallicus |
Short - Toed Snake-Eagle |
C |
NRM |
Varied habitats in warm regions |
LC |
|
|
5 |
Circus aeruginosus |
Eurasian Marsh Harrier |
C |
NRM |
Typically in extensive areas of marsh vegetation. |
LC |
|
|
6 |
Circus macrourus |
Pallid Harrier |
C |
CRM |
During breeding, found mainly on natural grassy plains and in
flat undulations. |
NT |
|
|
7 |
Circus pygargus |
Montagu's Harrier |
C |
HLM |
Open areas with grass or shrubs; generally flat or undulating
ground, less often in steeper terrain |
LC |
|
|
8 |
Elanus caeruleus |
Black Winged Kite |
C |
CRM |
Open grasslands with scattered bushes and small trees. |
LC |
|
|
9 |
Haliastur indus |
BrahminyKite |
C |
NRM |
Rivers, lakes, swamps, reservoirs, rice fields and urban areas |
LC |
|
|
10 |
Hieraaetus fasciata |
Bonelli'sEagle |
C |
NRM |
Mainly warm, sunny mountainous or broken terrain, normally with
cliffs. Vegetation. |
LC |
|
|
11 |
Hieraaetus pennatus |
Booted Eagle |
C |
CRM |
Forests and open areas. |
LC |
|
|
12 |
Ictinaetus malayensis |
Black Eagle |
C |
HLM |
Forested hills and mountains.
|
LC |
|
|
13 |
Milvus migrans |
Black Kite |
C |
NRM |
Ubiquitous, occurring from semi desert, grassland. |
LC |
|
|
14 |
Neophron percnopterus |
Egyptian Vulture |
C |
CRM |
Extensive open areas mainly in dry or arid region |
EN |
|
|
15 |
Pernis ptilorhynchus |
Oriental Honey Buzzard |
C |
CRM |
Wooded areas, preferring broad-leaved trees, in wide variety of
bio-climatic conditions |
LC |
|
|
16 |
Spizaetus cirrhatus |
Crested Hawk Eagle |
C |
HLM |
Deciduous, secondary forest and gallery forest. |
LC |
|
|
Family: Acrocephalidae |
|||||||
|
17 |
Acrocephalus dumetorum |
Blyth's Reed Warbler |
C |
CRM |
Adapted to varied habitats, not necessarily close to water. |
LC |
|
|
18 |
Acrocephalus stentoreus |
Clamorous Red Warbler |
C |
CRM |
Ponds and along rivers |
LC |
|
|
19 |
Iduna rama |
Sykes's Warbler |
C |
NRM |
Sand or clay deserts and semi-deserts with scattered vegetation.
|
LC |
|
|
Family: Aegithinidae |
|||||||
|
20 |
Aegithina nigrolutea |
Marshall's Iora |
O |
CRM |
Exclusively at plains level where favours thorny Acacia jungle |
LC |
|
|
21 |
Aegithina tiphia |
Common Iora |
O |
HLM |
Forest inhabited permanently. |
LC |
|
|
Family : Alaudidae |
|||||||
|
22 |
Ammomanes phoenicura |
RufousTailed Lark |
G,I |
NRM |
Dry open habitats with sparse vegetation; often found together
with other species |
LC |
|
|
23 |
Eremopterix griseus |
Ashy Crowned Sparrow Lark |
G,I |
NRM |
Dry open habitats with scattered low vegetation |
LC |
|
|
24 |
Galerida deva |
Sykes's Lark |
G,I |
HLM |
Dry, stony areas with sparse scrubby vegetation and dry
cultivation |
LC |
|
|
25 |
Mirafra erythroptera |
Indian Bushlark |
G,I |
NRM |
Arid, preferably somewhat scrubby and often rocky areas |
LC |
|
|
Family: Alcedinidae |
|||||||
|
26 |
Alcedo atthis |
Common Kingfisher |
C,I |
NRM |
Still or gently flowing water with plentiful small fish, and
with reeds, rushes or shrubs |
LC |
|
|
27 |
Cerylerudis |
Pied Kingfisher |
C |
NRM |
Small and large lakes, large rivers, estuaries, coastal lagoons,
mangroves and sandy and rocky. |
LC |
|
|
28 |
Halcyon smyrnensis |
White-Throated Kingfisher |
C,I,P |
All regions of
district |
Agricultural
areas and near water bodies |
LC |
|
|
Family : Anatidae |
|||||||
|
29 |
Anas poecilorhyncha |
Indian Spot-billed Duck |
feeds by dabbling for
plant food |
NRM |
Various types of wetlands |
LC |
|
|
Family: Apodidae |
|||||||
|
30 |
Apus nipalensis |
House Swift |
I |
NRM |
Familiar in towns and cities, though scarcer elsewhere. |
LC |
|
|
31 |
Cypsiurus balasiensis |
Asian Palm Swift |
I |
NRM |
Primary dependence on palms (Livistona, Borassus, Corypha) |
LC |
|
|
Family: Ardeidae |
|||||||
|
32 |
Ardeola grayii |
Indian Pond Heron |
C |
NRM |
Very varied, including rivers, streams, lakes, marshes, paddy
fields, reservoirs, tidal and mudflats |
LC |
|
|
33 |
Bubulcus ibis |
Cattle Egret |
I |
NRM |
All kinds of wet lands |
LC |
|
|
34 |
Egretta garzetta |
Little Egret |
C |
NRM |
Wide variety, frequenting all kinds of open wetlands, both
ephemeral and permanent, with shallow waters. |
LC |
|
|
Family: Bucerotidae |
|||||||
|
35 |
Ocyceros birostris |
Indian Grey Hornbill |
C,I |
NRM |
Deciduous and open thorn-forest |
LC |
|
|
Family: Campephagidae |
|||||||
|
36 |
Coracina melanoptera |
Black-headed Cuckooshrike |
F,I |
NRM |
Open forest, secondary growth, scrub-jungle; also in gardens,
orchards and hedgerows. |
LC |
|
|
|
Pericrocotus cinnamomeus |
Small Minivet |
I |
CRM |
Forest, woodland, mangrove forest, thorn-forest and casuarinas. |
LC |
|
|
|
Pericrocotus speciosus |
Scarlet Minivet |
I |
CRM |
Broadleaf, semi-evergreen and deciduous forests. |
LC |
|
|
Family: Caprimulgidae |
|||||||
|
39 |
Caprimulgus asiaticus |
Indian Nightjar |
I |
CRM |
Highly variable throughout range, but typically scrubland or
wooded country. Light scrub jungle. |
LC |
|
|
40 |
Caprimulgus atripennis |
Jerdon'sNightjar |
I |
NRM & CRM |
Mainly forest, deciduous forest, and dry forest. |
LC |
|
|
Family: Charadriidae |
|||||||
|
41 |
Vanellus indicus |
Red WattledLapwing |
I |
NRM |
Dry and open habitats, including cultivated and fallow fields
and wasteland. |
LC |
|
|
42 |
Vanellus malabaricus |
Yellow WattledLapwing |
I |
NRM |
Dry and open habitats, including cultivated and fallow fields
and wasteland. |
LC |
|
|
Family: Ciconiidae |
|||||||
|
43 |
Ciconia episcopus |
Woolly Necked Stork |
C,I |
NRM |
Open foraging in streams, pools, marshes, riverbanks. |
VU |
|
|
44 |
Ciconia nigra |
Black Stork |
C,I |
NRM |
Undisturbed open woodland, foraging in streams, pools, marshes,
and riverbanks |
LC |
|
|
45 |
Mycteria leucocephala |
Painted Stork |
C,P |
NRM |
Mostly frequents shallow freshwater at a diversity of wetland
types, such as lakes, grassy. |
NT |
|
|
Family: Cisticolidae |
|||||||
|
46 |
Orthotomus sutorius |
Common tailor bird |
I |
NRM |
Favors bushy cover by villages, gardens, and parks, even
shrubbery in city centers, and in forest area. |
LC |
|
|
47 |
Prinia buchanani |
Rufous fronted prinia |
I |
NRM & HLM |
Semi-desert plains and foothills with scrub, including dry
fields with scattered shrubs. |
LC |
|
|
48 |
Prinia hodgsonii |
Grey breasted prinia |
I |
NRM |
Favours scrubby areas in open forest, forest edge, riverside
thickets such asLantana |
LC |
|
|
49 |
Prinia inornata |
Plain prinia |
I |
CRM |
Scrubby grassland |
LC |
|
|
50 |
Prinia socialis |
Ashy prinia |
I |
NRM |
Bushy places, from scrubby grassland to garden shrubbery,
including Lantana thickets |
LC |
|
|
Family: Colubridae |
|||||||
|
51 |
Treron phoenicopterus |
Yellow-footed Green-pigeon |
F |
HLM |
Forest, scrubland, parks and gardens in lowlands and foothills;
avoids high mountains |
LC |
|
|
Family: Columbidae |
|||||||
|
52 |
Columba livia |
Blue rock pigeon |
G |
CRM & HLM |
Rocky sandstone and limestone plateau |
LC |
|
|
53 |
Spilopelia senegalensis |
Laughing dove |
F,G |
CRM |
Bushy places, from scrubby grassland to garden shrubbery |
LC |
|
|
54 |
Streptopeliadecaocto |
Eurasian collared dove |
F,G |
NRM |
inhabits semi-desert and arid regions |
LC |
|
|
|
Streptopelia tranquebarica |
Red collared dove |
G |
HLM |
Inhabits open country with trees, scrub, jungle and dry |
LC |
|
|
Family: Coraciidae |
|||||||
|
56 |
Coracias benghalensis |
Indian roller |
I |
NRM |
Open farmland, pasture, stubble, plantations, palm groves, dry Acacia and
Prosopisspp |
LC |
|
|
Family: Corvidae |
|||||||
|
57 |
Corvus macrorhynchos |
Large-Billed Crow |
F,O |
NRM |
Favors primary forest, in both lowlands and hills, and found
more locally |
LC |
|
|
58 |
Dendrocitta vagabunda |
Rufoustreepie |
C,I,O |
NRM |
Open deciduous woodland of all kinds, from dry forest to moist
broadleaf woodland |
LC |
|
|
Family: Cuculidae |
|||||||
|
59 |
Centropus sinensis |
Greater coucal |
C,I |
NRM |
Secondary forest, tall grassland, thickets, scrub near cultivation and paddy fields |
LC |
|
|
60 |
Clamator jacobinus |
Jacobin cuckoo |
I |
NRM & CRM |
Open woodland and scrub, dry thorn, thorny jungle, plains. |
LC |
|
|
61 |
Eudynamys scolopaceus |
Asian koel |
F,I |
NRM |
Open forest, and scrub, gallery forest, riverside scrub,
plantations |
LC |
|
|
62 |
Phaenicophaeus viridirostris |
Blue faced malkoha |
C,F,I |
NRM |
Secondary woodland, thorn scrub and bush, especially with Euphorbia
antiquorum. |
LC |
|
|
63 |
Phaenicophaeus leschenaultii |
Sirkeermalkoha |
C,F,I |
HLM |
Dry deciduous secondary forest, scrub and bush, with undergrowth
of lantana and thick grass, thorn. |
LC |
|
|
Family: Dicruridae |
|||||||
|
64 |
Dicrurus macrocercus |
Black drongo |
I |
NRM |
Mostly open country and farmland with scattered trees; very
common also in villages and suburbs |
LC |
|
|
Family: Emberizidae |
|||||||
|
65 |
Emberiza buchanani |
Grey-necked bunting |
G |
HLM |
Dry, rocky mountainsides, ravines and upland plateau, with
grassy clumps and weedy vegetation |
LC |
|
|
Family: Estrildidae |
|||||||
|
66 |
Amandava amandava |
Red avadavat |
I |
NRM |
Grassland, low marshy plains, damp grass, reeds, rice fields, sugar-cane
fields |
LC |
|
|
67 |
Lonchura malabarica |
Indian silverbill |
G,I |
NRM |
Open country, semi-desert and scrub, open dry woodland,
cultivated areas, and towns and villages |
LC |
|
|
68 |
Lonchura punctulata |
Scaly breasted munia |
G |
NRM |
Grassland with bushes, trees and scrub and rice fields. |
LC |
|
|
Family: Falconidae |
|||||||
|
69 |
Falco tinnunculus |
Common kestrel |
C |
NRM |
Adaptable to great variety of open or moderately wooded
terrains, normally with herbaceous |
LC |
|
|
Family: Hirundinidae |
|||||||
|
|
Cecropis daurica |
Red-rumped swallow |
I |
NRM & HLM |
Open hilly country and mountains, river gorges, |
LC |
|
|
71 |
Hirundo rustica |
Barn sparrow |
I |
NRM |
cultivation, human habitations |
LC |
|
|
72 |
Ptyonoprogneconcolor |
Dark crag martin |
I |
HLM |
Mountains, crags and coastal cliffs; also around human
habitations |
LC |
|
|
Family: Laniidae |
|||||||
|
73 |
Lanius vittatus |
Bay-backed shrike |
I |
NRM |
Variety of open, dry bushy areas with scattered trees, also
cultivated areas |
LC |
|
|
74 |
Lanius schach |
Long tailed shrike |
I |
CRM |
Open
country with scrub, and bushes, mainly in cultivated areas, also steppe areas |
LC |
|
|
75 |
Lanius meridionalis |
Southern grey shrike |
I |
NRM & CRM |
Fairly
open country dotted with thorny bushes in dry and warm, sunny lands |
VU |
|
|
Family: Leiothrichidae |
|||||||
|
76 |
Turdoides caudata |
Common babbler |
I |
|
Semi-desert,
dry plains, stony lower hills, xerophytic thorn scrub-jungle, scrubland,
sandy locations |
LC |
|
|
77 |
Turdoides affinis |
Yellow billed babbler |
I |
NRM |
Scrub,
secondary growth, thorn-jungle,
brushwood, scrub-covered eroded ravines |
LC |
|
|
Family: Meropidae |
|||||||
|
78 |
Merops orientalis |
Small Green Bee eater |
I |
NRM |
Arid
woodland with scattered trees on mainly bare soil or sand, and Acacia,
Commiphora |
LC |
|
|
Family: Monarchidae |
|||||||
|
79 |
Terpsiphone paradisi |
Asian paradise flycatcher |
I |
NRM |
Wide
range inhabits, deciduous mountain forest, shady and well-watered groves,
light forest |
LC |
|
|
Family: Motacillidae |
|||||||
|
80 |
Anthus hodgsoni |
Olive-backed pipit |
I |
NRM |
Breeds
on edge of taiga, on grassy and bracken-covered slopes, rocky ground |
LC |
|
|
81 |
Anthus campestris |
TwanyPipit |
I |
CRM |
Open
dry habitats, from sand dunes, sandy heaths, dry grassland and clear-felled
areas |
LC |
|
|
82 |
Anthus rufulus |
Paddy Field Pipit |
I |
NRM |
Open
country, short grassland, paddy fields, stubble fields and cultivations, also
airfields, |
LC |
|
|
83 |
Anthus similis |
Long-billed Pipit |
I |
|
|
LC |
|
|
84 |
Motacilla maderaspatensis |
White browed Wagtail |
I |
NRM |
Watercourses.
Favours streams and rivers, especially smooth-flowing rivers with rocks and
stony |
LC |
|
|
85 |
Motacilla cinerea |
Grey Wagtail |
I |
NRM |
Fast-flowing
mountain streams and rivers with riffles and exposed rocks |
LC |
|
|
Family: Muscicapidae |
|||||||
|
|
Copsychus saularis |
Oriental Magpie |
I |
NRM |
Dry deciduous forest but preferring presence of shady evergreen
trees. |
LC |
|
|
87 |
Ficedula parva |
Red Breasted Flycatcher |
I |
CRM |
Woodland, mainly mixed deciduous forest |
LC |
|
|
88 |
Monticola solitaries |
Blue rock Thrush |
I |
NRM & CRM |
Breeds on precipitous cliffs, in steep rocky valleys and
defiles, ravines and gorges, on crags |
LC |
|
|
89 |
Muscicapa dauurica |
Asian Brown Flycatcher |
I |
CRM |
Lowland open temperate and subtropical mature and secondary
broadleaf forests, secondary. |
LC |
|
|
90 |
Phoenicurus ochruros |
Black Redstart |
I |
NRM |
Sparsely vegetated rocky areas, including stony slopes with
xerophytic vegetation |
LC |
|
|
91 |
Saxicola caprata |
Pied bush Chat |
I |
HLM |
Open terrain with some low to mid-height vegetation |
LC |
|
|
92 |
Saxicola maurus |
Siberian Stonechat |
I |
CRM |
Open, usually rather barren landscapes. |
LC |
|
|
Family:Nectariniidae |
|||||||
|
93 |
Cinnyris asiaticus |
Purple Sunbird |
I,N |
NRM |
Usually around flowering shrubs and trees in dry and deciduous
forests, thorn-scrub, cultivation |
LC |
|
|
94 |
Leptocoma zeylonica |
Purple-rumpedSunbird |
I,N |
NRM |
Various types of forest and jungle, including secondary forest,
at forest edge |
LC |
|
|
Family: Passeridae |
|||||||
|
95 |
Passer domesticus |
House Sparrow |
G |
NRM |
Primarily associated with man, living around buildings from
isolated farms to urban centers |
LC |
|
|
Family: Phalacrocoracidae |
|||||||
|
96 |
Micro carboniger |
Little Cormorant |
C |
NRM |
Chiefly occupies bodies of fresh water in lowlands, including
ponds, rivers, lakes, swamps, canals |
LC |
|
|
Family: Phasianidae |
|||||||
|
97 |
Francolinus pondicerianus |
Grey Francolin |
G |
All regions of
district |
Grassland and semi-thorny scrub; dry rolling plains and plateau,
especially in areas near village. |
LC |
|
|
98 |
Pavo cristatus |
Indian Peafowl |
O |
CRM&HLM |
Open forest |
LC |
|
|
Family: Picidae |
|||||||
|
99 |
Dinopium benghalense |
Black-rumpdFlameback |
I |
CRM |
All types of moist to dry woodland, mostly deciduous; open
woodland and light forest |
LC |
|
|
Family: Ploceidae |
|||||||
|
100 |
Ploceus philippinus |
BayaWeaver |
G |
NRM |
Grassland, scrub with scattered trees, mangroves and cultivated
areas |
LC |
|
|
Family: Podicipedidae |
|||||||
|
101 |
Tachybaptus ruficollis |
Little Grebe |
I |
NRM |
Wide range of wetlands, normally small and shallow, including
small lakes, ponds, canals; |
LC |
|
|
Family: Psittaculidae |
|||||||
|
102 |
Psittacula krameri |
Rose-ringed Parakeet |
F |
NRM |
Chiefly deciduous habitats ranging from semi-desert to light
secondary jungle, mainly in lowlands |
LC |
|
|
Family:Pteroclididae |
|||||||
|
103 |
Pterocles exustus |
Chestnut bellied Sand Grouse |
G |
NRM & CRM |
Typically inhabits bare semi-desert, often with scattered thorny
scrubs or trees, e.g. Acacia. |
LC |
|
|
104 |
Pterocles indicus |
Painted Sand Grouse |
G |
NRM |
Bare foothills and plateau, sparsely covered with scrub or thorn
bushes of Acaciaspp |
LC |
|
|
Family: Pycnonotidae |
|||||||
|
105 |
Pycnonotus cafer |
Red-vented Bulbul |
G,F,N |
NRM |
Drier deciduous woodland, sparse secondary forest, scrub,
orchards and gardens, |
LC |
|
|
106 |
Pycnonotus luteolus |
White-browed Bulbul |
F,I |
NRM |
Open and largely cultivated habitats. Occurs in dry woodland
edge, second growth, scrub land |
LC |
|
|
Family: Recurvirostridae |
|||||||
|
107 |
Himantopus himantopus |
Black-wingedStilt |
I |
NRM |
Near water and wet lands |
LC |
|
|
Family: Saxicoloides |
|||||||
|
108 |
Saxicoloides fulicatus |
Indian Robin |
I |
NRM |
Palm groves, bare hillsides, open rocky places, newly burnt
clearings, cultivated fields |
LC |
|
|
Family: Scolopacidae |
|||||||
|
109 |
Actitis hypoleucos |
Common Sandpiper |
I |
NRM & CRM |
Prefers margins of water bodies, mostly riverbanks, preferably
with pebbles, sand or rocks |
LC |
|
|
110 |
Tringa ochropus |
Green Sandpiper |
I |
NRM & CRM |
Damp wooded areas |
LC |
|
|
Family: Strigidae |
|||||||
|
111 |
Athene brama |
Spotted Owlet |
I |
NRM |
Towns, agricultural fields, open forest, desert and semi-desert,
and mango groves, |
LC |
|
|
112 |
Bubo bubo |
Eurasian Eagle Owl |
C |
NRM |
Mostly inhabits areas of sparse human settlement or of
topographically inaccessible terrain |
LC |
|
|
Family: Sturnidae |
|||||||
|
113 |
Acridothres tristis |
Common Myna |
I |
NRM |
Open country, avoiding forest; dry open woodland, floodplains,
grasslands, cultivated areas |
LC |
|
|
114 |
Pastor roseus |
Rosy Starling |
I |
NRM & CRM |
pen steppes where orthopterans (locusts and other grasshoppers)
abundant |
LC |
|
|
115 |
Sturnia pagodarum |
BrahminyStarling |
F,I |
NRM & CRM |
Open deciduous forest, scrub, and cultivated areas near human
habitation; |
LC |
|
|
Family: Sylviidae |
|||||||
|
116 |
Chrysomma sinense |
Yellow eyed Babbler |
I |
NRM & CRM |
Scrub, secondary growth, thorn-jungle, tamarisks, brushwood,
scrub-covered eroded ravines, |
LC |
|
|
117 |
Sylvia althaea |
Hume's Whitethroat |
I |
NRM |
Broadleaf woodland |
LC |
|
|
118 |
Sylvia curruca |
Lesser Whitethroat |
I |
NRM & CRM |
open country or near forests in wide range of habitats rich in
dense |
LC |
|
|
Family: Tephrodornithidae |
|||||||
|
119 |
Tephrodornis pondicerianus |
Common WoodShrike |
I |
NRM & CRM |
Open forest, dry deciduous forest, secondary growth, bamboo
forest, woodland, scrub, orchards |
LC |
|
|
Family: Threskiornithidae |
|||||||
|
120 |
Threskiornis melanocephalus |
Black-headed Ibis |
C |
NRM, CRM & HLM |
Open country in marshes, swamps, flooded areas, margins of
rivers and lakes, paddy fields and fallow. |
NT |
|
|
Family: Timaliidae |
|||||||
|
121 |
Dumetia hyperythra |
Tawny-bellied Warbler |
G |
NRM & CRM |
Tall moist grasslands, rolling grassy hillsides, also roadside
patches of grassland |
LC |
|
|
Family: Turdidae |
|||||||
|
122 |
Turdus simillimus |
Indian Blackbird |
F,I |
NRM & CRM |
Deciduous and evergreen broadleaf forest, sholas, wooded
ravines, dense scrub |
LC |
|
|
Family: Turnicidae |
|||||||
|
123 |
Turnix suscitator |
Barred buttonquail |
G,I |
NRM, CRM & HLM |
Open grass and agricultural lands. |
LC |
|
|
Family: Upupidae |
|||||||
|
124 |
Upupa epops |
EusrasianHoo |
I |
NRM & CRM |
Open country such as pastures, parkland, sand-heath land, olive groves, vineyards |
LC |
|
Table 3. Feeding habits
of Birds in Anantapuramu District.
|
Feeding habit |
Total
number of species |
|
Carnivore |
26 |
|
Frugivores |
2 |
|
Granivore |
10 |
|
Insectivore |
55 |
|
Omnivore |
3 |
|
Carnivore
, Frugivores and insectivore |
2 |
|
Carnivore and Insectivore |
5 |
|
Carnivore,
Insectivore and Omnivore |
1 |
|
Carnivore,
Insectivore and Piscivore |
1 |
|
Carnivore
and Piscivore |
1 |
|
Frugivores and
Granivore |
2 |
|
Frugivores and
Insectivore |
5 |
|
Frugivores and
Omnivore |
1 |
|
Granivore, Frugivores
and Nectarnivore |
1 |
|
Granivore and
Insectivore |
6 |
|
Insectivore and Nectarnivore |
2 |
|
Others |
1 |
|
Total |
124 |
Discussion
Anantapuramu district is a semi-arid and rain shadow
region with extremes of temperature during summer. Districts vast area and
natural geographical division’s makes avian habitat architecture more complex
which perhaps supports more species as they provide more resources and
opportunities for microhabitat segregation thus more species may co-occur per
unit area, leading to a positive correlation between biological diversity and
structural diversity. Most of the reserve forests are tropical dry deciduous,
southern tropical thorn forests; vegetation cover is uniformly distributed in
the district, and mostly concentred in central and high altitude mandals. Hence,
richness and avifaunal diversity is greater in these regions. Vegetation is a potential factor in
determining bird community composition.
Research studies have found physiognomic attributes of vegetation such
as foliage height diversity, foliage volume and percent vegetation cover has a
direct correlation with bird species richness and diversity foraging ecology of
birds often is limited by foliage structure.
This district is mostly dependent on
dry agro economy, which is evident from LULC (Land Use Land Cover) images of
the district; similarly agriculture land, water bodies and plantation are
increasing from the year 2005. It is the good sign for agro economy which
further has direct implication on the increased percentage of insectivorous and
carnivorous birds due excellent availability of pests like caterpillars, large
insects, lizards, mice and bird’s eggs and nestlings. Our observations on
Seasonal changes, frequent drought conditions and change in agricultural
pattern might have brought new adaptations in food habit of some insectivorous
birds like Cattle egret, Small green bee-eater, Blue-tailed bee-eater, Common
myna, Bank myna, Indian tree pie, Red-vented bulbul, Pied myna, Magpie robin,
Black drongo, Jungle babbler, Pied crested cuckoo, Gray - headed myna, King
fisher, Flycatcher, Large pied wagtail, Owl and Jungle crow
(Ali,
1990). In this district there is increased percentage of insectivorous
birds is due to its bests feeding adaptations suited to the agricultural
practice in the district. Ali
(1990) emphasised feeding behaviour of
birds depends on various environmental factors such as geographical location,
habitat, seasons, water quality, competition (intraspecific and interspecific)
and scarcity of food. Observations on role of birds in agriculture pest control
has reveled many species of caterpillars and moths were controlled
by Magpie robin (Copsychus saularis),
Black drongo (Dicrurus adsimilis) and
Jungle babbler (Turdoides striatus).
Weevils were eaten by Indian treepie (Dendrocitta
vagabunda). Large-pied wagtail (Motacilla
maderaspatensis) was found to control the aphid. Owl, House crow (Corvus splendens) and Jungle crow (Corvus macrorhynchos) control the
increasing populations of most
destructive pest like rats and mice.
Crabs, destructive to paddy, were eaten by Corvus splendens and Bubulcus
ibis. Grasshoppers and small insects
were eaten by Small green bee eater (Merops
orientalis), Blue-tailed bee eater (Merops
philippinus), Common myna (Acridotheris
tristris), Bank myna (Acridotheris ginginianus),
Indian tree pie (Dendrocitta vegabunda),
and Red-vented bulbul (Pycnonotus cafer)
(Inskipp
and Inskipp 1985, Ali 1990, Richard 1993, Subba 2001).Waste land
has decreased subsequently, in the year 2005 waste land area which was 2367.47
sq/km, in 2012 it was 2160.54 and in 2015 it is 1344.34 sq/ km. From LULC
analysis in 2015 waste land was converted into scrub. Forest cover is not much
changed as most of the forest area is declared as reserved forest. Positive correlation was observed in waste,
scrub and forest land which may be attributed to frugivore bird’s population
which are important components of forest ecosystem, as they influence plant
regeneration through seed dispersal, however, foraging behaviour of birds may
influence their effectiveness as dispersers. Similarly, insectivorous birds are
important components of ecosystem they may control population of insects.
From LULC maps we identify that
built up area is increasing gradually in the year 2005, total built up area was
234.4 sq/km,in 2012 area which was 373.54 and in 2015 it is increased up to
410.43 Sq.km. the this negative correlative changes can be attributed to the
anthropogenic pressure on ecosystem is increasing due to technological
advancements and government incentives on establishment of industrial parks,
acquiring huge land for SEZ (Special Economic Zones), establishment of wind
mills in wildlife areas and reserve forests, quarrying, blasting of hilly
areas, indiscriminate use of agricultural pesticides, unrestricted grazing of
livestock’s in reserve forests, and burning of grasslands, habitat
fragmentation, loss of habitat, are prominent threats for avian fauna. Apart
from this weather and rainfall also play a major role in the disturbing balance
of ecosystems functionalities. Considering the significant role of Avifauna in
monitors the ecological balance, there is greater need for
the formulation of effective conservation policies (Nautiyal 2013).
CONCLUSION
The present study is an attempt in providing baseline
information for devising further conservation strategies, especially keeping in
view dry land regions such as Anantapuramu district in Andhra Pradesh.
Acknowledgment
We extend our sincere thanks to the Forest Department of Anantapuramu
district, Andhra Pradesh for supporting us to carry out this study. The authors
would also like to thanks to the faculty of Department of Zoology, Sri
Krishnadevaraya University, Anantapuramu for their assistance during research
work.
References
Abdulali, H., 1945. Birds of the Vizagapatnam District. J. Bomb. Nat. Hist. Soc., 45(3), 333-347.
Ali,
S., Ripley, S.D. and Dick, J.H., 1983.A pictorial guide to the birds of
the Indian subcontinent, Bombay natural
History Society, Oxford University Press, India.
Ali, S., 1990. The book
of Indian birds. Oxford University Press, pp. 187.
Anand, M., 2000. Birds in and
around Sri Venkateswara Wildlife Sanctuary. Zoos’ Print J., (10),
339–343. http://dx.doi. org/10.11609/JoTT.ZPJ.15.10.339-43
Arlott, N., 2014. Collins Field Guide: Birds of India, Harper Collins
Publisher, London, pp. 400.
Champion,
H.G. and Seth, S.K., 1968. A Revised Survey of the Forest Types of
India.Government of India Publication, New Delhi.
David, J.P., Murugan, B.S. and Mankadan, R.,
2011. Frugivory birds and mammals in
Sri Harikota Island, southern India. J.
Bomb. Nat. Hist. Soc., 108(1), 24-40.
Emlen,
J.J. 1974. An Urban Bird Community in Tucosan, Arizona: Diversity, Structure
and Regualtion. Condor, 76,184-194.
ENVIS
online. 2016. Global Biodiversity
Hotspots With Special Emphasis on Indian Hotspots.http://bsienvis. nic.in/Database/Biodiversity-Hotspots-in-India_20500.
aspx
Grimmett, R.,
Inskipp, C. and Inskipp, T., 2000. Pocket Guide to
the Birds of the Indian Subcontinent. Oxford University Press, New Delhi, India,
pp. 384.
Inskipp, C. and Inskipp, T., 1985. A Guide to the Birds of Nepal, Croom
Helm, London.
Kannan, V., Manakadan, R., Rao, P., Mohapatra,
K.K., Sivakumar, S. and Santharam, V., 2008.The water birds of Pulicat Lake, Andhra Pradesh - Tamil Nadu, India,
Including those of the adjoining wetlands andheronries. J. Bomb. Nat. Hist. Soc., 105(2), 162-180.
Manakadan, R. and Pittie, A. 2001. Standardised common and scientific names of the birds
of the Indian subcontinent. Buceros-Envis Newsletter, 6(1): 1-37.
MoEF and Kalpavriksh, 2004. Profile of Biodiversity in India,
Nat.Biodiversity Strategy and Action Plan,India:FinalTech.Report of the
UNDP/GEF Sponsored Project. MoEF, Govt. of India, & Kalpavriksh, New
Delhi/ Pune. http://www. kalpavriksh.org/images/Biodiversity/Bio_NBSAP/Chapter4.pdf.
Nautiyal,
S., Bhaskar, K., Khan, Y.D.I and Venkateshalu 2013. Biodiversity Monitoring and
its Distribution in and Around Uranium Mining Area of Gogi, Gulbarga (Yadgir),
Karnataka: A Case Study, J. Biodiv., 4(2), 69-77.
Narayana, B.L., Rao, V.V. and Pandiyan, J.,
2013. Avifaunal assemblages in relation
to different croplands/habitats of Nalgonda District, Andhra Pradesh, India.International J. Life Sci. Biotechnol.
and Phar. Res., 2(3), 212-224.
Nautiyal, S., Bhaskar, K. and Khan, Y.D.I.
2015. Biodiversity of Semiarid Landscape: Baseline Study for Understanding the
Impact of Human Development on Ecosystems. Springer International Publishing,
398.
Prasad, K.K., Krishna, B.R., Srinivasulu, C. and
Srinivasulu, B., 2014. Avifaunal Diversity
of Manjeera Wildlife Sanctuary, Andhra Pradesh, India. J. Threat. Taxa, 6(2),
5464–5477. http://dx.doi. org/10.11609/ JoTT.o3505.5464-77.
Pullaiah, T. and Yesoda, N. 1989. Flora of Anantapur District, Andhra Pradesh,
India. Bishen Singh Mahendra Pal Singh, Dehra Dun, India.
Richard,
1993. The Collins Bird Atlas. https://trove.nla.
gov.au/version/171754269
Rajashekara,
S. and Venkatesha, M.G., 2015. Temporal and Spatial avian community composition
in urban landscapes of the Bengaluru region, India. J. Environ. Biol., 36, 607-616.
Ripley, S.D., Beehler, B.M. and Raju, K.S.R.K.
1987–88. Birds
of Visakhapatnam Ghats, Andhra Pradesh (Part 1-2). J.
Bomb. Nat. Hist. Soc., 84(3) & 85(1):
540-559, 90-107.
Sinha, R.K., Dubey, M., Tripathi, R.D., Kumar,
A., Tripathi, P. and Dwivedi, S., 2010. India as a Megadiversity
Nation.Archives of enviro news - Newsletter of ISEB India., 16(4) Online. https:// isebindia.com/09-12/10-11-3.html.
Srinivasulu, C., 2004. Birds of Kawal Wildlife Sanctuary, Andhra Pradesh, India. J. Bomb. Nat. Hist. Soc., 101(1), 3-25.
Srivastava, Dayawanti et al. (ed.) (2010). "States and
Union Territories: Andhra Pradesh: Government". India 2010: A Reference Annual (54th ed.).
New Delhi, India: Additional Director General, Publications
Division, Ministry of Information and Broadcasting
(India), Government of India. pp. 1111–1112.
Subba, B. R. 2001. Garden Birds. Info Science, 1(5).
Subramanyam, V.V.B and Khan, Y.D.I. 2016. Avian
Fauna of proposed wind power project area at Chillavaripalli and Ellutla
reserve forests; J. Entomol. Zool. Stud., 4(6), 722-728.
Subramanyam, V.V.B., 2017a. A Preliminary assessment and diversity of
birds in Ramagiri east and west forest, Ananthapuram District, Andhra Pradesh,
India. Int. J. Zool. Stud., 2(4), 21-28.
Subramanyam, V.V.B., 2017b. Herpatofaunal
diversity in Chillavaripalli and Ellutla reserve forests of Anantapuramu
district, Andhra Pradesh. Int. J. Fauna Biol.
Stud., 4(5), 93-98.
Subramanyam, V.V.B. and Khan, Y.D.I., 2017. Diversityof
mammalian fauna and conservation issues of the Anantapuramu district of Andhra
Pradesh, India. Int. J. Rec. Sci. Res., 8(12),
22646-22652.
Sutherland,
W.J., 2006. Ecological census Techniques – A hand book, Second edition,
Cambridge university press, Cambridge, UK, pp. 432.