Journal of Threatened
Taxa | www.threatenedtaxa.org | 26 December 2023 | 15(12): 24443–24446
ISSN 0974-7907
(Online) | ISSN 0974-7893 (Print)
https://doi.org/10.11609/jott.8624.15.12.24443-24446
#8624 | Received 03
July 2023 | Final received 24 October 2023 | Finally accepted 28 November 2023
First confirmed record of Arabian
Gazelle Gazella arabica Lichtenstein,
1827
(Mammalia: Artiodactyla:
Bovidae) on Masirah Island,
off the coast of eastern Oman in the Arabian Sea
Taimur Al Said 1, Haitham Al
Rawahi 2, Maha
Al Ansari 3, Al Mutasim Al Hinai 4, Ahmed Al Amri
5,
Ahmed Al Wahaibi
6 ,
Ghasi Al Farsi 7 , Saud Al Wihibi 8 &
Salman Al Farsi 9
1–9 Environment Authority, P.O Box
323, Muscat, P.C. 100, Sultanate of Oman.
1 taimur_a_alsaid@hotmail.com
(corresponding author), 2 haitham.alr88@gmail.com, 3 maha.s.alansari@hotmail.com,
4 almutasim90@gmail.com, 5 ahmedamri87@gmail.com, 6 ahmed.alwahaibi150@gmail.com,
7 ghasi.alfarsi@hotmail.com, 8 saudalwahibi60@gmail.com, 9
alfarsisalman908@gmail.com
Editor: David Mallon, Manchester Metropolitan
University, Manchester, UK. Date of publication: 26 December
2023 (online & print)
Citation: Al Said, T., H. Al Rawahi, M. Al Ansari, A.M.
Al Hinai, A. Al Amri, A. Al
Wahaibi, G. Al Farsi, S. Al Wihibi
& S. Al Farsi (2023). First confirmed record of Arabian Gazelle Gazella arabica Lichtenstein, 1827 (Mammalia:
Artiodactyla: Bovidae) on Masirah Island, off the coast of eastern Oman in the
Arabian Sea. Journal
of Threatened Taxa 15(12): 24443–24446. https://doi.org/10.11609/jott.8624.15.12.24443-24446
Copyright: © Al Said et al. 2023. Creative Commons Attribution 4.0 International
License. JoTT
allows unrestricted use, reproduction, and distribution of this article in any
medium by providing adequate credit to the author(s) and the source of
publication.
Funding: The National Survey of Biodiversity is fully funded by the Environment Authority of Oman.
Competing interests: The authors declare no competing interests.
Acknowledgements: The National Survey of
Biodiversity is one of the objectives of the 2040 vision of Oman. This survey
was made possible by the permission of the Chairman of the Environment
Authority, H.E Dr Abdullah bin Ali Al Amri
and under the direction of Mr. Zahran Al Abdulasalam,
the Office for Conservation of the Environment, Environment Authority. Special
thanks to the Environment Center of Wilayat Masirah under the
direction of Mr. Majid Al Arami and the staff for
their help. Furthermore, thanks to the department of Environment Control
including the rangers: Mr. Yousuf Al Ghidani, Mr. Samer Al Naabi, and Mr. Mazin Al Ghusaini, for further
assistance. Finally, yet importantly the Administration and Finance Departments
for their help in logistics and administration work.
Abstract: In Oman, the Arabian Gazelle Gazella arabica is known to be distributed in
the Hajar mountains of the north, desert plains in central of Oman, and Jabal Samhan foothills & Nejd
area in the south. We report the first confirmed record of the Arabian Gazelle
on Masirah island, 15 km off the mainland of eastern
Oman. This finding was part of a national survey of biodiversity in Oman in
which 29 camera traps were set to survey the majority of the island which
covers about 400 km2. Only two camera traps detected Arabian
Gazelle, in an area covering only 22 km2. The survey on the island
suggests that the population is small and isolated. Future research studies are
required both in the field of ecology and genetics.
Keywords: Camera trapping, conservation,
Mountain Gazelle, Sultanate of Oman, ungulate.
The Arabian Gazelle Gazella arabica is one of the five ungulate
species that occur in Oman along with the Arabian Oryx Oryx
leucoryx, Arabian Tahr Arabitragus jayakari,
Nubian Ibex Capra nubiana, and Arabian Sand
Gazelle Gazella marica
(Mallon & Kingswood 2001; Al Hikmani
et al. 2015). Arabian Gazelle was previously known as Mountain Gazelle Gazella gazella
before the species was split into two genetically distinct lineages
(Lerp et al. 2013). The adult males and females have an average body weight of
22.5 kg and 18.3 kg, respectively, whilst the adult male has larger and thicker
neck and horns compared to the adult female (Horwitz et al. 1990). The species
is distributed across the Arabian Peninsula in arid and semi-arid environments
(Harrison & Bates 1964). In Oman, they usually occur in habitats where the Vachellia tortilis
(= Acacia tortilis; ‘simr’ in Arabic) trees appear, which they use as shade and
feed on their leaves and seed-pods. Arabian Gazelles are usually found in both
plains and rugged mountains but are likely to avoid rocky areas (Al Jahdhami et al. 2017). The species may once have been found
in far north of Oman in Musandam governorate, but today they are likely to be
locally extinct (Al Hikmani et al. 2015). Northern
populations of Arabian Gazelles in Al Batinah governorate have also disappeared but smaller populations still exist in the
foothills of the Hajar mountains (Al Hikmani et al.
2015). The Arabian Oryx Sanctuary in Al Wusta
governorate previously held the largest population of Arabian Gazelles in
Arabia with an estimate of 10,000 gazelles, but currently holds a small
population (Mallon & Kingswood 2001; Al Hikmani et al. 2015; Al Jahdhami
et al. 2017; Alsaid et al. 2019). In the south of
Oman in Dhofar governorate, the Arabian Gazelle once occurred all over the arid
areas such as the northern foothills known as (the ‘Nejd’), the gravel plains
south of the Empty Quarter, and the southern coastal plain and plateau of the
arid Jabal Samhan massif.
It has never been reported in the monsoon habitats on Jabal
Al Qamar and Jabal Al Qara.
Today, only a small population exists in the Nejd and the southern coastal
plains between Mirbat and Sadah
(Al Hikmani et al. 2015). A more recent joint survey
was conducted by the Office for Conservation of the Environment and the
Ministry of Environment in 2019 on the gazelle population in Dhofar in the area
running from Thumrait to Demeet.
The survey area was approximately 1,547 km2 and consisted of flat
rolling plains, and wadis. Distance sampling and analyses were used to collect and process line transect data. The population
estimate for the area was calculated as 127 gazelles (). Ras As Shagar Nature Reserve and As Saleel Natural Park have the
healthiest and largest wild populations of Arabian gazelle (Al Hikmani et al. 2015; Al Jahdhami
et al. 2017; Ross et al. 2019). Threats such as habitat loss, habitat
fragmentation, road kills and mainly poaching have caused population declines
over the past few years. However, Oman remains the stronghold for Arabian
Gazelle since the highest wild population resides in the country, due to
conservation efforts (Mallon & Kingswood 2001;
Strauss et al. 2009; Al Hikmani et al. 2015; Al Jahdhami et al. 2017).
Interestingly, reviews of the
status and distribution of mammals in the Arabian Peninsula do not mention the
presence of Arabian Gazelles on Masirah Island
(Harrison & Bates 1964; Harrison 1968). Furthermore, the International
Union for Conservation of Nature (IUCN) Red List also does not include Masirah island within the Arabian Gazelle distribution
range. However, the BirdLife International Data Zone
contains information on a bird survey conducted on Masirah
Island in 1980 which reported a list of key bird species and non-bird species
on the Island. They listed Cape Hare Lepus capensis
jefferyi as being endemic to Masirah
island and Mountain Gazelle Gazella gazella as present (BirdLife
International 2023), although to date there has been no confirmed evidence
(e.g., specimen, photograph).
The study area is Masirah Island (Figure 1) which lies in Ash Sharquiyah governorate and is Oman’s largest island. It
lies 15 km off the mainland in the Arabian Sea. The total area of the island is
649 km2 and has a human population of 12,000 who are mostly
concentrated in the north of the island where the Royal Air Force of Oman has a
base (Abdul-Wahab et al. 2020). The island consists of a combination of
mountains, cliffs and plains where the highest peak— Jabal
Ash Shabbah lies north-east of the island at an
altitude of ~210 m (Jansen 2023). The average annual rainfall is approximately
70 mm (Kwarteng et al. 2009).
A total of 29 camera traps (Spypoint & Bushnell) were placed by wildlife biologists
and rangers of the Environment Authority on 4–18 December 2022. They were
installed on rocks or boulders facing animal pathways and resting areas at a
height of 0.25–0.75 m above the ground to survey large and medium mammals. The
cameras used normal infrared sensors to trigger a three-photograph burst with a
5 s delay between captures. The camera trap sampling area was approximately 400
km2 (Figure 1).
Here we describe the first
confirmed photographic sighting of Arabian Gazelle on Masirah
using camera traps. The gazelles were photographed on the north-eastern cliffs
of the island. Both camera traps (NM24) and (NM25) photographed a male Arabian
Gazelle on 7 January and 22 February 2023 respectively (Image 2). Moreover, on
6 December 2022 during the camera trap survey conducted by the Environment
Authority, remains of an Arabian Gazelle foot were found close to where the
camera traps photographed both gazelles (Image 3). There were also recent
sightings by locals in the area. Regardless of a fairly large camera trapping
survey, only two individuals were captured by camera traps in an area covering
only 22 km2. This indicates that the population may be both small
and isolated. It is difficult to know the reason for the populations’ small
size, however this population on Masirah island could
be genetically different from the rest of the Arabian Gazelle population.
Currently, an ongoing camera trap survey is being conducted on the island and
this will provide a better understanding of their current distribution and
population size. Further research on their genetics is required and therefore a
plan is currently being designed to collect fecal pellets, tissue, and bone
from the remains of dead Arabian Gazelle for genetic analysis to determine any
genetic differences with the remaining Arabian Gazelle population in Oman.
Another future research for the Arabian Gazelle in Masirah
island would be to have a long-term camera trap study in place to understand
their population status and distribution. Setting global positioning system
(GPS) collars on Arabian Gazelle would allow us to gain an understanding of
their home range estimation, movement patterns, and resource selection.
For
images - - click here for full PDF
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