Grey Junglefowl Gallus Sonneratii (Galliformes: Phasianidae) in Kalakad-Mundanthurai Tiger Reserve, Tamil Nadu, India

 

K. Muthamizh Selvan 1 & N. Sridharan 2

 

Wildlife Institute of India, Chandrabani,Post box No 18, Dehradun, Uttarakhand 248001, India

Email: 1 km.selvan6@gmail.com (corresponding author), 2 sridharanavc@gmail.com

 

 

Date of publication (online): 26 January 2012

Date of publication (print): 26 January 2012

ISSN 0974-7907 (online) | 0974-7893 (print)

 

Editor: Rahul Kaul

 

Manuscript details:

Ms # o2538

Received 05 August 2010

Final received 29 June 2011

Finally accepted 18 November 2011

 

Citation: Selvan, K.M. & N. Sridharan(2012). Grey Junglefowl Gallus Sonneratii (Galliformes: Phasianidae) in Kalakad-Mundanthurai Tiger Reserve, Tamil Nadu, India. Journal of Threatened Taxa 4(1): 2328Ð2329.

 

Copyright: © K. Muthamizh Selvan& N. Sridharan2012. Creative Commons Attribution 3.0 UnportedLicense. JoTT allows 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 would like to thank The Director, Dean and Research co-ordinatorof Wildlife Institute of India, Directorate of Project tiger, Team of all India tiger monitoring programme, Tamilnaduforest department for logical support and permission and also like to thank Dr.Saravanan, Mr. Sajan John for their helps during manuscript preparations. Special thanks to anonymous reviewers.

 

 

For figure, table -- click here                                          

 

Grey Junglefowl Gallus sonneratii is endemic to southern peninsular India and is listed as Least Concern (Birdlife International 2009) and under Schedule II by CITES.  Grey or SonneratÕs Junglefowl (GJ) is distributed throughout southern peninsular India (Grimmett et al. 1998).  Very few studies have been conducted on the Grey Junglefowl and these mainly pertain to abundance (Ramesh 1994; Sathyakumar2006; Sathyanarayana 2007) and habitat use (Tata & Gautam 1993; Zacharias 1997; Subramanian et al. 2002; Sathyanarayana 2002; Satyakumar2006).  Most of the populations of GJ within protected areas in India are not monitored.  Sathyanarayana (2007) has reported the need for research on the current status and distribution and habitat requirements of this species.  GJ has a declining trend in population due to hunting for meat, egg depredation by local communities (Gubbi 2006), poaching and habitat degradation (Sathyanarayana 2007).  This study was undertaken to estimate the abundance of GJ in the Kalakad-Mundandurai Tiger Reserve (K-MTR) in the southern Western Ghats.

Study Area: Kalakad-MundanduraiTiger Reserve (K-MTR, 895km2, 8025ÕÐ8053ÕN & 77010ÕÐ77035ÕE),forms the catchment area for 14 rivers and streams.  The vegetation types range from scrub montaneto wet evergreen, all within an elevational range of 40 to 1866 m with an annual rainfall of 2000mm (Vasudevanet al. 2001).  The maximum temperatures at the site range from 17 to 28 0C and the minimum temperature from 14 to 19 0C. The period from October to January is usually cold and misty (Ganesh & Davidar 1999).  This reserve has many endemic, threatened fauna and flora (Johnsingh 2001).

Methods:Field sampling was carried out in the months of September 2007 to November 2007.  During this period permanent transects were established across different vegetation types. Transects were established in Kannikatti (3), Sengaltheri (2), Mundanthurai(2), Kakachi (1), Kodamadi(2) and Oothu (1).  Each transect was surveyed thrice by two observers between 0600Ð0900 hr.  Each transect differed in length, the average transect length being 1.8km.  Group size, sex, sighting distance and angle every time the species was detected wererecorded.  Opportunistic encounters during the study were only used to calculate the sex ratio of the GJ.  To estimate the density of the species we used Distance 5.0. Release 2 (Thomas et al. 2006).

Results and Discussion: A total of 59.7km transect was surveyed during our fieldwork in K-MTR and 97 individuals were recorded on all the transects.  The calculated density of the GJ was 25.45±3.4 km-2.  The average group size was 1.5±0.09, the encounter rate of GJ was 1.07km-1 and the sex ratio of GJ in K-MTR was 1:1.4.

Probability of sighting varied according to the habitats.  Sathyakumar(2006) found the GJ at 34.42km-2 only in Mundanthuraiplateau and an overall mean density 19.78 individual km-2.  In TheniForest Division the density reported was 37.03km-2 (Sathyanarayana 2007).

GJ prefer moderate canopy cover, high scrub cover and mixed deciduous forest to scrub forest (Nirmala& Vijayan 2002).  According to the present study the group size of GJ was 1.5 to 1.9 which is comparable with earlier observations in K-MTR (1.0Ð1.6 km-2; Sathyakumar2006).  GJ is not gregarious like the Red Junglefowl and the maximum group size sighted was three individuals during our field work.  Encounter rate was 1.07km-2 whichwas slightly higher than (0.8km-2) Sathyakumar(2006) study.

 

 

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