Journal of
Threatened Taxa | www.threatenedtaxa.org | 26 September 2018 | 10(10):
12425–12428
Additional
field records provide further resolution of the distribution of the Water
Monitor Varanus salvator (Squamata: Varanidae) in
northwestern Myanmar
Steven G. Platt 1, Myo
Min Win 2 & Thomas R.
Rainwater 3
1,2 Wildlife Conservation Society -
Myanmar Program, No. 12, Nanrattaw St., Kamayut Township, Yangon, Myanmar
3 Tom Yawkey
Wildlife Center & Belle W. Baruch Institute of Coastal Ecology and Forest
Science, Clemson University, P.O. Box 596, Georgetown, South Carolina 29442,
USA
1 sgplatt@gmail.com, 2
4nge86@gmail.com, 3 trrainwater@gmail.com
(corresponding author)
doi: https://doi.org/10.11609/jott.4425.10.10.12425-12428 | ZooBank:
urn:lsid:zoobank.org:pub:8AED5B33-C658-4538-89DF-165BCA7D3A77
Editor: Anonymity requested. Date
of publication: 26 September 2018 (online & print)
Manuscript details: Ms # 4425 |
Received 23 July 2018 | Final received 11 September 2018 | Finally accepted 15
September 2018
Citation: Platt, S.G., M.M.
Win & T.R. Rainwater (2018).
Additional field records provide further resolution of the distribution of the
Water Monitor Varanus salvator
(Squamata: Varanidae)
in northwestern Myanmar. Journal
of Threatened Taxa 10(10): 12425–12428; https://doi.org/10.11609/jott.4425.10.10.12425-12428
Copyright: © Platt 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: Andy Sabin; The Andrew Sabin Family Foundation;
The Critical Ecosystems Partnership Fund.
Competing interests: The authors declare no competing interests.
Acknowledgements: We thank the Minister of the Ministry of Environmental
Conservation and Forestry, Director General and Deputy Director General of the
Planning and Statistics Department of the Ministry of Environmental
Conservation and Forestry, Director General and Deputy Director General of the
Forest Department and the Director of NWDC for their dedication to wildlife
conservation in Myanmar and allowing us to conduct fieldwork in northern
Myanmar. We are grateful for the field
assistance provided by Tun Win Zaw,
Naing Win Aung, and Zaw Naing Oo. Support was provided by
Andy Sabin and the Andrew Sabin Family Foundation, and the Critical Ecosystems
Partnership Fund. TRR was supported by the Yawkey
Foundation and Clemson University.
We are indebted to Than Myint for securing the
necessary permits and permission to conduct fieldwork. Finally, we are grateful to Lewis Medlock for
advice on camera trapping, Flora Ihlow and Levinson
Deb for assistance with obtaining literature, and Kyaw
Zay Yar for preparing our
map. This paper represents technical
contribution number 6655 of the Clemson University Experiment Station.
Despite being one of the most common and widely
distributed varanids in South and Southeast Asia
(Bennett et al. 2010; Das 2010; Chan-ard et al.
2015), the distribution of the Water Monitor Varanus
salvator (Laurenti,
1768) within Myanmar remains poorly delineated, particularly for the central
and northern regions of the country (Cota et al.
2009; Sai Sein Lin Oo & Bates 2016).
Smith (1935) stated that V. salvator
was “plentiful throughout Burma” [now Myanmar] without mentioning any specific
localities. Anderson (1878) and Boulenger (1888) reported specimens of V. salvator from the Bhamo and
the Kachin Hills, respectively. Cota et al. (2009)
suggested these earlier records could be in error, perhaps representing
specimens obtained in markets or transported as food, and further noted that
extensive collecting by research teams from the California Academy of Sciences
failed to record V. salvator anywhere in
central and northern Myanmar. More
recently, Oo & Bates (2016) confirmed the
occurrence of V. salvator in north-central
Myanmar after photographing a large adult in Bhamo
and finding a locally-collected specimen being offered for sale at a market in Banmauk, about 140km west of Bhamo
(Fig. 1). Sai
Sein Lin Oo
& Bates (2016) concluded these records either (1) represent an isolated and
perhaps relict occurrence or (2) the distribution of V. salvator
extends up the Ayeyarwady River and its tributaries.
We herein present two additional photo records, which further
document the distribution of V. salvator
within northwestern Myanmar (Fig. 1).
The first record was obtained on 26 April 2016 when one of us (MMW)
photographed a juvenile (total length [TL] ca. 90–100 cm) V. salvator while traveling by boat along Nam Pi Lin
Stream (25.6830N & 95.6360E; elevation ca. 100m) in Sagaing Region (Image 1).
The monitor was basking on a log extending from a steep bank and
over-hanging the stream, and dropped into the water as the boat
approached. Nam Pi Lin Stream is encompassed
within the boundaries of Htamanthi Wildlife
Sanctuary. The habitat along this
section of the stream is dense riparian forest and bamboo thickets
transitioning into old-growth evergreen forest with increasing elevation away
from the water. Additional information
on the vegetation and physiography of Htamanthi
Wildlife Sanctuary is provided by Beffasti & Galanti (2011).
The second photo record was obtained when a large adult V.
salvator (TL ca. 150cm) was “captured” on a game
camera deployed about 0.25km south-east of Limpha Village (25.8080N & 95.5360E;
elevation ca. 132m) in Sagaing Region. The game
camera (Moultrie Series A) was set in a densely vegetated seasonal swamp along
the Chindwin River beside the carcass of a young domestic Water Buffalo Bubalus bubalis
(Linnaeus, 1758) that had perished after becoming mired in deep mud. The motion-sensitive game camera (programed
to take three photographs at 1-min intervals) was deployed from 17 February to
6 March 2018 (17 trap-nights) and captured a sequence of six images (1324-1326 hr) of a Water Monitor on 1 March (Images 2A–F). The first image shows the monitor with head
and neck extended back and upwards in a near-vertical position usually
exhibited when swallowing (Image 2A).
The monitor then investigates the remains of the carcass (Image 2B–C)
and moves across and away from the camera (Image 2D–F). At the time these photographs were taken the
buffalo carcass consisted of little more than bones in a pool of fetid muck
(Stage 6 of Payne 1965).
Our photo records from Nam Pi Lin Stream and Limpha Village extend the known distribution of V. salvator in Myanmar approximately 170km north and
westwards of the recent records from Bhamo and Banmauk (Oo & Bates
2016). Collectively, these records
strongly suggest the distribution of V. salvator
extends up the Ayeyarwady and Chindwin Rivers into
northern and northwestern Myanmar. We
see no reason to assume these records represent an isolated relict occurrence
of V. salvator in northern Myanmar as
suggested by Sai Sein Lin Oo & Bates (2016).
Given the lack of apparent geographic barriers to dispersal, we further
suggest the distribution of V. salvator
extends at least as far north as the Hukaung Valley
in Kachin State.
Obviously additional investigation will be required to resolve these biogeographical questions.
Our photo records of V. salvator
appear to be assignable to the subspecies V. salvator
macromaculatus Deraniyagala
1944, which until recently was thought to be restricted to Thailand (Koch et
al. 2007; Cota et al. 2009; Sai
Sein Lin Oo & Bates
2016). Although considerable
inter-population variation is evident in V. salvator
macromaculatus (Cota
et al. 2009), the two individuals in our photo records exhibit attributes
consistent with this subspecies, namely, 1) brownish dorsal background color
with at least five transverse rows of ocelli and
light dotting between rows, 2) light chin with prominent crossbands
on snout, 3) light ventral surface with six dark, sharply pointed bars on
lateral surface, and 4) anterior tail with transverse rows of light spots and ocelli, and posterior tail with distinctive alternating
light and dark crossbands (Koch et al. 2007). Similarly, Sai Sein Lin Oo & Bates (2016)
concluded the two specimens they examined in northern Myanmar were assignable
to V. salvator macromaculatus. Finally, our experience highlights the
potential for using automated game cameras for documenting the occurrence and
behaviors of varanids (see also Ariefiandy
et al. 2013; Bennett & Clements 2014).
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