Hostname: page-component-76fb5796d-r6qrq Total loading time: 0 Render date: 2024-04-30T03:57:34.592Z Has data issue: false hasContentIssue false

Assessing the status of the Green Peafowl’s “expected stronghold” in dry forests along the Salawin River, north-west Thailand

Published online by Cambridge University Press:  02 September 2022

Niti Sukumal*
Affiliation:
Conservation Ecology Program, King Mongkut’s University of Technology Thonburi, 49 Soi Thian Thale 25, Bang Khun Thian Chai Thale Road, Tha Kham, Bang Khun Thian, Bangkok 10150, Thailand
Somying Thunhikorn
Affiliation:
Department of National Parks, Wildlife and Plant Conservation, 61 Phaholyothin Road, Chatuchak, Bangkok 10900, Thailand
Tommaso Savini
Affiliation:
Conservation Ecology Program, King Mongkut’s University of Technology Thonburi, 49 Soi Thian Thale 25, Bang Khun Thian Chai Thale Road, Tha Kham, Bang Khun Thian, Bangkok 10150, Thailand
*
*Author for correspondence: Niti Sukumal, Email: niti_230@hotmail.com

Summary

The suitable habitats of the Endangered Green Peafowl Pavo muticus have declined by 80% over the past century due to extensive anthropogenic degradation. Currently, only six strongholds remain in mainland South-east Asia. While there are estimates of the species’ presence and status in five of these, the sixth one, defined as an “expected stronghold” located in the suitable dry forest along the Salawin River between Thailand and Myanmar, is not well documented. This study assessed the status of the area as a stronghold for the Green Peafowl’s long-term survival by estimating 1) the population density, 2) the current extension of suitable habitats, and 3) the threats to its survival. The area had an estimated density of 0.27 calling males/km2 (CI = 0.07–1.01) inhabiting 9,154 km2 of a mosaic of forest types, including mixed dry pine, mixed deciduous, and dry dipterocarp forests. Higher estimates were reported in other strongholds, including 0.8 birds/km2 in Bago Yoma (Myanmar), 15.8 birds/km2 in north-east Thailand, 1.13–11.34 birds/km2 in HuaiKhaKhaeng Wildlife Sanctuary (Thailand), 0.15–1.7 birds/km2 in northern Cambodia, and 0.15–4.69 birds/km2 in eastern Cambodia / south-central Vietnam. Hunting, habitat disturbance, and the presence of humans posed the greatest danger to the species across the surveyed area. Our results confirm the potential of the area for the species’ long-term survival. However, this “expected stronghold,” which could sustain a population of over 10 calling males/km2 like other high-quality strongholds, is in dire need of a comprehensive management plan to help reduce anthropogenic pressure. Ultimately, transboundary management between Thailand and Myanmar is crucial for the long-term repopulation of this stronghold.

Type
Research Article
Copyright
© The Author(s), 2022. Published by Cambridge University Press on behalf of BirdLife International

Access options

Get access to the full version of this content by using one of the access options below. (Log in options will check for institutional or personal access. Content may require purchase if you do not have access.)

Footnotes

The authors dedicate this paper to the memory of Atthapol Sunsernboon, ranger at HuaiOo Substation, DoiWiangLa Wildlife Sanctuary, who assisted during data collection.

References

BirdLife International (2018) Pavo muticus. The IUCN Red List of Threatened Species 2018: e.T22679440A131749282. https://doi.org/10.2305/IUCN.UK.2018-2.RLTS.T22679440A131749282.en. [accessed 09 May 2021].CrossRefGoogle Scholar
Brickle, N. W. (2002) Habitat use, predicted distribution and conservation of Green Peafowl (Pavo muticus) in DakLak Province, Vietnam. Biol. Conserv. 105: 189197.CrossRefGoogle Scholar
Buckland, S. T., Anderson, D. R., Burnham, K. P., Laake, J. I., Borchers, D. L. and Thomas, L. (2001) Introduction to distance sampling: Estimating abundance of biological population. New York, USA: Oxford University Press.Google Scholar
Burnham, K.P. and Anderson, D.R. (1998) Model selection and interference: A practical Information-theoretic approach. New York, USA: Springer.CrossRefGoogle Scholar
Cronin, D. T., Dancer, A., Long, B., Lynam, A. J., Muntifering, J., Palmer, J. and Bergl, R. A. (2021) Application of SMART software for conservation area management. Pp. 201224 in: Wich, S. A. and Piel, A. K., eds. Conservation technology. Oxford: Oxford University Press, UK.CrossRefGoogle Scholar
Delang, C. (2005) The political ecology of deforestation in Thailand. Geography 90: 225237.CrossRefGoogle Scholar
Win, Lay, Sukumal, N., Shwe, N.M. and Savini, T. (In review) Teak plantations are an effective corridor for Green Peafowl movement within the fragmented Bago Yoma range, central-south Myanmar. Ornithol. Applic.Google Scholar
Loveridge, R., Kidney, D., Ty, S., Eames, J. C., Borchers, D., Kidney, D. and Borchers, D. (2017) First systematic survey of Green Peafowl Pavo muticus in north eastern Cambodia: reveals a population stronghold and preference for disappearing riverine forests. Cambodian J. Nat. Hist. 2017: 157–167.Google Scholar
Nuttall, M., Nut, M., Ung, V. and O’Kelly, H. (2016) The first abundance estimates for the Endangered Green Peafowl Pavo muticus in Cambodia: identification of a globally important site for conservation. Bird Conserv. Internatn. 27: 127139.CrossRefGoogle Scholar
Paul, A. L. (2018) With the Salween Peace Park, we can survive as a nation: Karen environmental relations and the politics of an indigenous conservation initiative. Thesis. York University, Toronto, Canada.Google Scholar
Pearson, R. G. (2007) Species’ distribution modeling for conservation educators and practitioners. Synthesis. Washington DC: American Museum of Natural History, Lessons in Conservation. Available from: http://ncep.amnh.org.Google Scholar
R Development Core Team (2014) R: A language and environment for statistical computing. Vienna, Austria: R Foundation for Statistical Computing. http://www.R-project.org.Google Scholar
Ratnam, J., Tomlinson, K. W., Rasquinha, D. N. and Sankaran, M. (2016) Savannahs of Asia: antiquity, biogeography, and an uncertain future. Trans. Roy. Soc. B 371: 20150305.CrossRefGoogle Scholar
Saridnirun, G., Sukumal, N., Grainger, M. J. and Savini, T. (2021) Living with human encroachment: status and distribution of Green Peafowl in northern stronghold of Thailand. Glob. Ecol. Conserv. 28: e01674.CrossRefGoogle Scholar
Savini, T., Namkhan, M. and Sukumal, N. (2021) Conservation status of Southeast Asian natural habitat estimated using Galliformes spatio-temporal range decline. Glob. Ecol. Conserv. 29: e01723.CrossRefGoogle Scholar
Shwe, N. M., Sukumal, N., Oo, K. M., Dowell, S., Browne, S. and Savini, T. (2021) Importance of isolated forest fragments and low intensity agriculture for the long term conservation of the Green Peafowl Pavo muticus. Oryx 55: 311317.CrossRefGoogle Scholar
Simcharoen, S., Thongnamchaima, B., Sukmasuong, R., Thobmongkol, P., Khoothong, M., Sunthran, C., Mheesangpraew, Y., Thongooppagarn, W. and Singkram, P. (1995) Population and distribution range of Green Peafowl (Pavo muticus) in HuaiKhaKhaeng Wildlife Sanctuary. Wildl. J. Thailand 4: 4348. (In Thai).Google Scholar
Sodhi, N. S., Koh, L. P., Brook, B. W. and Ng, P. K. L. (2004) Southeast Asian biodiversity: an impending disaster. Trends Ecol. Evol. 19: 654660.CrossRefGoogle ScholarPubMed
Sukumal, N., McGowan, P. J. K. and Savini, T. (2015) Change in status of Green Peafowl Pavo muticus (Family Phasianidae) in Southcentral Vietnam: A comparison over 15 years. Glob. Ecol. Conserv. 3: 1119.CrossRefGoogle Scholar
Sukumal, N., Dowell, S. D. and Savini, T. (2017) Micro-habitat selection and population recovery of the Endangered Green Peafowl Pavo muticus in western Thailand: implications for conservation guidance. Bird Conserv. Internat. 27: 414430.CrossRefGoogle Scholar
Sukumal, N., Dowell, S. D. and Savini, T. (2020a) Modelling occurrence probability of the Endangered Green Peafowl in mainland Southeast Asia: applications for landscape conservation and management. Oryx 54: 3039.CrossRefGoogle Scholar
Sukumal, N., Grainger, M. J. and Savini, T. (2020b) Long-term persistence of Endangered Green Peafowl differs according to level of human disturbance. Bird Conserv. Internat. 30: 210219.CrossRefGoogle Scholar
Swaddle, J. P., Francis, C. D., Barber, J. R., Cooper, C. B., Kyba, C. C., Dominoni, D. M., Shannon, G., Aschehoug, E., Goodwin, S. E., Kawahara, A. Y. and Luther, D. (2015) A framework to assess evolutionary responses to anthropogenic light and sound. Trends Ecol. Evol. 30: 550560.CrossRefGoogle ScholarPubMed
Tak, C., Crouthers, R., Sukumal, N., Chhin, S. and Savini, T. (2022). Importance of Srepok Wildlife Sanctuary, Cambodia, for the endangered green peafowl: implications of co-occurrence near human use areas. Raffles Bull. Zool. 70:249256.Google Scholar
Thomas, L., Buckland, S. T., Rexstad, E. A., Laake, J. L., Strindberg, S., Hedley, S. L., Bishop, J. R. B., Marques, T. A. and Burnham, K. P. (2010) Distance software: design and analysis of distance sampling surveys for estimating population size. J. Appl. Ecol. 47: 514.CrossRefGoogle ScholarPubMed
Zuur, A. F., Ieno, E. N. and Elphick, C. S. (2010) A protocol for data exploration to avoid common statistical problems. Meth. Ecol. Evol. 1: 314.CrossRefGoogle Scholar
Supplementary material: File

Sukumal et al. supplementary material

Table S1

Download Sukumal et al. supplementary material(File)
File 17 KB