Population density and
group size of the Grey Junglefowl Gallus sonneratii in the MelghatTiger Reserve, Maharashtra, central India
K. Narasimmarajan 1, Bidyut B. Barman 2 & Lalthan Puia 3
1,2,3 Post Box
No: 18, Wildlife Institute of India, Chandrabani,
Dehradun, Uttarakhand 248001, India
Email: 1 wildlife9protect@gmail.com
(corresponding author), 2 bidyutb8@gmail.com, 3 lalthanpuia24@gmail.com
Date of publication (online): 26 July 2012
Date of publication (print): 26 July 2012
ISSN 0974-7907 (online) | 0974-7893 (print)
Editor: Rajiv Kalsi
Manuscript details:
Ms #
o2821
Received 03 June 2011
Final received 05 June 2012
Finally accepted 29 June 2012
Citation: Narasimmarajan,
K., B.B. Barman & L. Puia (2012). Population density
and group size of the Grey Junglefowl Gallus sonneratii in the MelghatTiger Reserve, Maharashtra, central India . Journal of Threatened Taxa 4(7): 2723–2726.
Copyright: © K. Narasimmarajan,Bidyut B. Barman & Lalthan Puia 2012. Creative Commons Attribution
3.0 Unported License. JoTTallows unrestricted use of this article in any medium for non-profit purposes,
reproduction and distribution by providing adequate credit to the authors and
the source of publication.
Acknowledgements: We
thank the Director and Dean, Wildlife Institute of India. We would like to thank Mr. A.K. Mishra,
field director and other forest department staff in MelghatTiger Reserve for their help for every support and accommodation. We personally
thanked Dr. K. Ramesh for his valuable comments in earlier draft of the manuscript, we gratefully acknowledged the anonymous
referees and special thanks to Dr. R.S. Kalsi for his
positive comments during the editing. We also extend our thanks to our field
assistants and driver for their dedication during the field
work.
For figures, images, tables -- click here
Avian community studies are effective
tools for monitoring forest ecosystems. Birds are widely recognized as good bioindicatorsof the quality of the ecosystems and the health of the environment (Gill
1994). They are responsive to
change; their diversity and abundance can reflect ecological trends in other biodiversities (Furness & Greenwood 1993). Because of their highly specific habitat
requirements, birds are increasingly intolerant of even slight ecosystem
disturbances (Schwartz & Schwartz 1951). Work on forest bird communities has been
done in other parts of the country from time to time (Ramakrishnan1983; Johnsingh et al. 1987, 1994). The Grey Junglefowl(GJ), endemic to peninsular India, is listed as Least Concern in status
(Birdlife International 2012). Although, there have been several studies on the GJ in southern India,
there are no reported studies on its population density and group size in the Melghat Tiger Reserve (Galliformsof India 2007). Hence this study
was conducted as a preliminary investigation to find out the population density
of the GJ in Melghat Tiger Reserve.
Study area: Melghat Tiger Reserve established in 1973, is
situated in the southern offshoot of the Satpuramountain range (20051’–21046’N & 76038’–
77033’E). The total
tiger reserve area of about 1676.93km2 including critical tiger habitat
area of 361.28km2* (*Gugamal division) is
lies in two districts, Akola and Amravati in Maharashtra (Chandrakaret al. 2007; Narasimmarajan et al. 2011). The Melghat region experiences tropical climate with
temperatures ranging between 130C in winter and 450C
during summer. The annual
rainfall ranges between 1000 and 2250 mm. A total of 715 plant species were recorded in the MelghatTiger Reserve (Mahabal 2005). The survey was carried out in three
ranges of Gugamal division in the MelghatTiger Reserve, which is Dhargad,Dhakna and Chikaldara with
the area surveyed about 250km2 (Image 1).
Material and Methods: Population densities and group size of
the GJ were estimated by the line transect method using Distance Sampling
(Burnham et al. 1980; Buckland et al. 1993, 2001). We walked 34 line transects (2km
length), each having five temporal replicates to record the encounter rate of
GJ. On every walk, we recorded
sightings, group size, sighting angle using a hand held compass (KB 20, Santo,
Vantaa, Finland), and sighting distance using laser range finder (Bushnell,
Overland Park, Kansas, USA). We
laid 170 circular plots in order to describe and evaluate the impact of biotic
disturbance and emphasis habitat preference of the GJ. Five circular plots were laid at each
transect having a 20m radius at a distance of every 400m. On every plot, data on trees, shrubs,
herbs, grass and leaf litter cover, human disturbance, tree lopping,
wood/bamboo cutting, people seen and the presence of human trail were recorded
(Johnsingh 1987; Sathyakumar2006). A total of 170 circular
plots were laid in order to estimate the impact of biotic disturbance on the
GJ, habitat and habitat preferences were also investigated during the survey
period. The disturbances were subjectively
categorized into highly disturbed (0.75–1), moderately disturbed
(0.50–0.75), less disturbed (0.25–0.50) and least disturbed
(0–0.25), respectively. Data
of the circular plots (n=170) were pooled to estimate the Mean (±SE) of factors
associated with biotic disturbances. Pooled line transect data were used to estimated the population density
and group size of GJ using program DISTANCE 5.0 (Thomas et al. 2006).
Results and Discussion: Population
density: A total of 36 GJ sightings comprising 114
individuals were recorded during (total effort 170 transect walks) the entire
study period. An overall density of GJ 16.72±4.70 Birds/km2, (n =
36) the average group density was 5.68±1.49, (n = 36) whereas the average
cluster size was 2.95 birds (n = 36), P = 0.5157 (Table 1). Best fit model
(Hazard/Hermite) was chosen on the basis of minimum
AIC = 248.55. The encounter rate of GJ 0.39±0.2/km2 was also
determined from the analysis (Fig. 1). The highest number of GJ recorded in a sighting was five individuals and
the least was one individual among all the sightings recorded and mean group
size was 3.16 individuals. Studies conducted elsewhere on the GJ have shown
different estimates of population density. Subhani et al. (2000) estimated an overall
density of 7.87 birds/km2 in Deva VetalaNational Park and Das (2006) estimated density of 5.39 birds/ha in Rajaji National Park. The variation in density estimates in different studies could be due to
the differences in methodology and habitat in the study areas besides many
other factors may influence such as season, annual variations and observer
differences.
Habitat
preference and biotic disturbance:In the Melghat Tiger Reserve, GJs were generally
observed in areas having mixed deciduous forest with Tectona grandis and Dendrocalamus strictus. Other species in this habitat included Terminalia tomentosa, Anogeissus latifolia, Butea monosperma, Emblica offficinalis, Boswellia serrata, Ougeinia oojeinensis, Laegerstromia parviflora, Lantana camara and Ziziphus mauritiana(Champion & Seth 1968), which probably helped in camouflage for the
GJ in the study area (Johnsingh 1987, 1994; Sathyakumar 2006). Estimated biotic disturbance indicators were Mean±SEof tree cutting 0.25±0.07, presence of human trails 0.16±0.02, number of trees
lopped 0.05±0.08, grass/bamboo cutting 0.02±0.01 and people seen 0.01±0.02
recorded from the study area (Fig. 2).
Johnsgard (1986) reported that the GJ inhabits a
wide variety of habitats, from secondary dry deciduous to moist evergreen forests,
but is especially common in bamboo thickets, edges of village forests around
cultivated fields and around clearings or neglected plantations. In the Periyar Tiger Reserve, GJ have been sighted frequently near
human inhabitations but they were absent in the high hills (Zacharias
1997). The species showed a
preference for areas with a mix of slopes, hilly, plains as well as the less
forested areas and open grassland patches (Subramanian et al. 2008). Consequently the MelghatTiger reserve, GJs were encountered mostly in areas having dense mixed
deciduous forests where the biotic disturbances were in low intensity. They avoided human habitations and high
hills with open areas.
Habitat preference is a dynamic process
in the natural systems. Many species
are confined to specific habitat types (Winkler & Leisler1985). Based on our observations,
we suggest that human disturbance, cattle grazing and tree/grass cutting
activities were probably the major threats to the species in this area. This has probably pushed the GJ back in
to the dense shrubby areas of the Tiger reserve. Further study is needed to understand
the ecology and conservation threats of the species in MelghatTiger Reserve.
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