Please note, this National Red List website contains a subset of data whilst we transition to national focal point driven data uploads. We thank you for your patience with this and welcome national contributors to get in touch to update their national dataset. Terms of Use including citation guidance are found here.

The previous dataset is available via: https://archive.nationalredlist.org/. This site is no longer updated but can help with most enquiries whilst we focus on redevelopment.

NT

Assessment ID
329894
Taxon name
Rhizoprionodon acutus
(Rüppell, 1837)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Rhizoprionodon acutus
(Rüppell, 1837)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
carcharhinidae
Genus
Rhizoprionodon
Species
acutus
Species authority
(Rüppell, 1837)
Taxonomic notes and synonyms listed
Molecular evidence supports the idea that Rhizoprionodon acutus is a complex of (at least) four species that needs further taxonomic investigation (Naylor et al. 2012).
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Milk Shark occurs throughout UAE waters. It is very commonly taken in a wide range of artisanal, subsistence and commercial fisheries, and is often the dominant shark species in landings in the UAE. Inshore fishing pressure is intense and intensifying in parts of the Arabian Sea, and its abundance is suspected to have declined due to fishing. Though data specifically from the UAE are not available, individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. Given the intense fishing pressures faced by this species throughout the Arabian Seas (and until recently, in the UAE), and ongoing threats from bycatch and habitat loss, it is inferred that declines reported in the Arabian Seas are representative of the status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by 20-30% over the past three generation lengths, or about 15 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2cd.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Milk Shark occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific and Eastern Atlantic Oceans (Last and Stevens 2009).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
The Milk Shark is a common continental shelf species that mostly inhabits muddy waters in coastal areas to about 50 m depth (Weigmann 2016). Across its range, it is reported to reach a maximum size of 178 cm, however, in the Arabian Seas region, the largest specimen recorded is 98 cm TL (Jabado et al. 2015). Females reach maturity between 59.7-74 cm TL and males between 60-76.5 cm TL (Henderson et al. 2006, Moore et al. 2012, Jabado et al. 2015, Shaaban et al. 2018, Sen et al. 2018). Off northwest India, it reaches maturity at the end of its second year and is a moderately fast-growing species of shark (Sen et al. 2018). Its natural mortality rate off northwest India was estimated as 0.61 year<sup>-1</sup> (Sen et al. 2017). It has a very productive life history being born at around 35-37 cm TL, maturing at young ages (2-3 years), producing 2-8 young every year and living up to 10 years (Henderson et al. 2006, Kizhakudan et al. 2015). Generation length is estimated at 5.25 years (Compagno 1984, Last and Stevens 1994).
Threats and conservation measures listed
Threats listed in assessment
In the UAE, sharks have been impacted by targeted commercial fisheries until 2014 when a ban on export of sharks was imposed (Ministry of Climate Change and Environment). Sharks continue to be impacted by artisanal and bycatch fisheries (Annual Fisheries Statistical Report for Abu Dhabi Emirate 2001-2018), though catch data are not species-specific. Marine habitats in the region have experienced high levels of disturbance and are quickly deteriorating due to major impacts from development activities (Sheppard <em style=""font-variant-ligatures: normal;font-variant-caps: normal;orphans: 2; text-align:start;widows: 2;-webkit-text-stroke-width: 0px;text-decoration-style: initial; text-decoration-color: initial;word-spacing:0px"">et al. 2010).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
329891
Taxon name
Nebrius ferrugineus
(Lesson, 1831)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Nebrius ferrugineus
(Lesson, 1831)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
orectolobiformes
Family
ginglymostomatidae
Genus
Nebrius
Species
ferrugineus
Species authority
(Lesson, 1831)
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Tawny Nurse Shark occurs throughout UAE coastal waters, and is presumably naturally uncommon there. This species is not targeted or valued in markets of the UAE. It is taken as bycatch in some areas of the Arabian Sea region (Sri Lanka and India), and declines have been noted. Slow life history characteristics, including low fecundity and a low annual rate of population increase causes the species to have a low capacity to recover from even moderate levels of exploitation. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net, longline and trawl fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. Though data specifically from the UAE are not available, individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. It is inferred that declines reported in the Arabian Sea region are representative of its status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by 20-30% over the past three generation lengths, or about 90 years. It is listed as Vulnerable A2cd.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Tawny Nurse Shark occurs throughout UAE waters (Jababo et al. 2015). Globally, it is widespread in the Indo-West Pacific.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
The Tawny Nurse Shark occurs on or near coral reefs, particularly in crevices and caves, and seagrass lagoonal habitat at depths of less than 70 m. The species reaches a maximum length of at least 320 cm total length (TL), with males maturing at 250 cm TL and females at 230-290 cm TL. This species is ovoviviparous (aplacental viviparity), giving birth to 1-4 pups per litter (Teshima et al. 1995, Compagno 2001), and size at birth is 40-80 cm TL. Generation length is estimated at 30 years based on age data from Ginglymostoma cirratum (Carrier and Luer 1990).
Threats and conservation measures listed
Threats listed in assessment
In the UAE, this species is not directly targeted by fisheries, but may be discarded as bycatch throughout the Arabian Gulf. This species is impacted by bycatch fisheries that are active elsewhere in its range. Marine habitats in the Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010). Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
329890
Taxon name
Mobula eregoodoo
(Cantor, 1849)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Mobula eregoodoo
(Cantor, 1849)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
myliobatiformes
Family
mobulidae
Genus
Mobula
Species
eregoodoo
Species authority
(Cantor, 1849)
Taxonomic notes and synonyms listed
Combined morphological and molecular data led Last et al. (2016) and White et al. (2017) to conclude that Mobula eregoodootenkee is a junior synonym of M. kuhlii. However, Hosegood et al. (2019) suggested these were separate species, which was supported by Notarbartolo di Sciara et al. (2020), who also clarified the nomenclature as M. eregoodoo.
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2d
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Longhorned Pygmy Devil Ray occurs throughout UAE waters and may be locally common there. There is a total ban on fishing for this species in UAE waters. It may be a synonym of Mobula kuhlii according to some workers. It is a component of the bycatch in several fisheries, but much of this catch is unreported. It is directly targeted in Sri Lanka (if it occurs there) and India, and exported to international markets, especially China where the gill plates are highly-valued. When captured in the Red Sea and Arabian Gulf, it is typically discarded alive, and significant declines are not suspected there at this time. Its low productivity causes it to be susceptible to rapid population declines when experiencing exploitation. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net, longline and trawl fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. Though data specifically from the UAE are not available, individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. It is inferred that declines reported in the Arabian Sea region are representative of its status in the UAE. Based on recorded levels of exploitation, it is suspected to have declined by 20-30% over the past three generation lengths, or about 23 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2d.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Longhorned Pygmy Devil Ray occurs throughout UAE waters. Globally, it is widespread in the tropical Indo-West Pacific (Notarbartolo di Sciara et al. 2017).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
This ray is not known to penetrate the epipelagic zone. Mating and birthing occur in shallow water, and juveniles remain in these areas. The Longhorned Pygmy Devil Ray reaches a maximum size of approximately 100 cm disc width (DW). The neotype for this species, a male of 96.9 cm DW, was sexually mature (Notarbartolo-Di-Sciara 1987). These rays are ovoviviparous (uterine viviparity), usually producing one offspring per litter. Intrinsically, Manta and Mobula rays have among the lowest productivity of any chondrichthyan (Pardo et al. 2016). As there is not enough data to estimate an exact generation length for this species, an approximate, suspected generation length is used. A midway point of 7.5 years between a very conservative low of five years, and the larger Spinetail Devil Ray's 10-year generation length is suspected to be the approximate generation length for the Longhorned Pygmy Devil Ray until more accurate information becomes available (Cuevas-Zimbron et al. 2013).
Threats and conservation measures listed
Threats listed in assessment
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by target (for fins and their valuable meat) and bycatch fisheries that are active elsewhere in its range. Manta rays are easy to target because of their large size, slow swimming speed, aggregation behaviour and predictable habitat use.
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
329889
Taxon name
Loxodon macrorhinus
Müller & Henle, 1839
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Loxodon macrorhinus
Müller & Henle, 1839
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
carcharhinidae
Genus
Loxodon
Species
macrorhinus
Species authority
Müller & Henle, 1839
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Sliteye Shark occurs throughout UAE inshore waters. It is caught in inshore gill net, trawl and line fisheries throughout the Arabian Sea region. Inshore fishing pressure is intense and intensifying, and declines are known in some areas. Though data specifically from the UAE are not available, individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. Given the intense fishing pressures faced by this species throughout the Arabian Seas, ongoing threats from bycatch and habitat loss, it is inferred that declines reported in the Arabian Seas are representative of the status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by 20-30% over the past three generation lengths, or about 15 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2cd.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Sliteye Shark occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Last and Stevens 2009).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
The Sliteye Shark is a small species that occurs near the bottom on continental and insular shelves to depths of 100 m (Jabado and Ebert 2015). The young are born at 40 to 45 cm, and males mature around 67 cm TL (Jabado et al. 2016), and grow to a maximum of 95 cm (Anderson and Ahmed 1993). It reproduces annually usually with a litter size of 2-4. Ageing work in Australia has demonstrated that it grows quickly, reaching maturity at 1.5 to 2 years of age, with a female maximum age of ~9 years (Gutteridge et al. 2013). Its generation length is estimated to be 5.15 years.
Threats and conservation measures listed
Threats listed in assessment
In the UAE, sharks have been impacted by targeted commercial fisheries until 2014 when a ban on export of sharks was imposed (Ministry of Climate Change and Environment). Sharks continue to be impacted by artisanal and bycatch fisheries (Annual Fisheries Statistical Report for Abu Dhabi Emirate 2001-2018), though catch data are not species-specific. Marine habitats in the region have experienced high levels of disturbance and are quickly deteriorating due to major impacts from development activities (Sheppard <em style=""font-variant-ligatures: normal;font-variant-caps: normal;orphans: 2; text-align:start;widows: 2;-webkit-text-stroke-width: 0px;text-decoration-style: initial; text-decoration-color: initial;word-spacing:0px"">et al. 2010).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
329886
Taxon name
Chiloscyllium griseum
Müller & Henle, 1838
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Chiloscyllium griseum
Müller & Henle, 1838
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
orectolobiformes
Family
hemiscylliidae
Genus
Chiloscyllium
Species
griseum
Species authority
Müller & Henle, 1838
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Grey Bamboo Shark occurs throughout UAE coastal waters, but it is poorly known in part due to taxonomic uncertainty and confusion with Chiloscyllium arabicum. It is not targeted, but is taken as bycatch in trawl (and other) fisheries, and is typically discarded due to its small size and low market value. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net, longline and trawl fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. Though data specifically from the UAE are not available, individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. It is inferred that declines reported in the Arabian Sea region are representative of its status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by 20-30% over the past three generation lengths, or about 27 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2cd.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Grey Bamboo Shark occurs throughout UAE waters. In the Arabian Seas region, it is known from a few specimens from the Arabian Gulf, Iran, Pakistan, India and Sri Lanka. Its global distribution is uncertain due to confusion with other species, but is known to occur in the Indo-West Pacific.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
This species is a sluggish inshore bottom dweller found on sandy and muddy bottoms, on rocks and in coral lagoons at depths from 5 to 100 m (Weigmann 2016). It is oviparous and deposits eggs in small oval egg cases on the sea floor. The maximum size is at least 77 cm total length (TL). Free-living individuals have been found at sizes of at least 12.2 cm, and size at hatching uncertain. Males mature between 45 and 55 cm TL. The species feeds mainly on small fish, shrimps, worms, molluscs and crabs. Age data are not available, but generation length is estimated as 9 years using data from the similar-sized White-spotted Bambooshark (C. plagiosum) (Chen et al. 2007).
Threats and conservation measures listed
Threats listed in assessment
In the UAE, sharks have been impacted by targeted commercial fisheries until 2014 when a ban on export of sharks was imposed (Ministry of Climate Change and Environment). Sharks continue to be impacted by artisanal and bycatch fisheries (Annual Fisheries Statistical Report for Abu Dhabi Emirate 2001-2018), though catch data are not species-specific. This species is impacted by bycatch fisheries that are active elsewhere in its range. Marine habitats in the Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010). Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
329884
Taxon name
Carcharhinus macloti
(Müller & Henle, 1839)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Carcharhinus macloti
(Müller & Henle, 1839)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
carcharhinidae
Genus
Carcharhinus
Species
macloti
Species authority
(Müller & Henle, 1839)
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2bcd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Hardnose Shark occurs throughout UAE inshore and offshore waters. It is caught in subsistence, artisanal and commercial fisheries that utilize gillnets, lines and trawls throughout the Arabian Sea region. Inshore fishing pressure is intense throughout this species' range, and the highest levels of exploitation probably occur in the UAE, Iran, Pakistan and India. Although of small size, its life history may not be as productive as that of other small carcharhinids (e.g., Rhizoprionodon spp.), making it more susceptible to fishing pressure. Anecdotal information indicates that significant declines have occurred over the past 20 years in UAE waters. Individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. Given the intense fishing pressures faced by this species throughout the Arabian Seas, and ongoing threats from bycatch and habitat loss, it is inferred that declines reported in the Arabian Seas are representative of the status in the UAE. Based on fish market observations over time, recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by 20-30% over the past three generation lengths, or about 24 years. It nearly meets the thresholds for Vulnerable under criterion A2bcd, and is listed as Near Threatened.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Hardnose Shark occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific, but has not been recorded from the Gulf of Aden or the Red Sea (Last and Stevens 2009).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
The Hardnose Shark is a small species of carcharhinid that occurs in inshore and offshore waters to depths of 170 m (Ebert et al. 2013). The species reaches a maximum size of 99 cm total length (TL) in the region (Jabado et al. 2015, Raje et al. 2015). Young are born at a relatively large size (47-49 cm TL), with females maturing at 81 cm TL and males at 75 cm TL (Jabado et al. 2015). Mature females probably have a two-year reproductive cycle, with only 2-3 pups produced per litter (Henderson et al. 2004, Jabado et al. 2016). Smart et al. (2013) reported in Australian waters that maximum age was about 12 years with maturity around 4 years. This suggests a generation length of 8 years. Based on these life history parameters it is likely to have a much lower level of productivity than other small species of carcharhinid sharks (e.g., Rhizoprionodon spp.) and so is more susceptible to fishing pressure.
Threats and conservation measures listed
Threats listed in assessment
In the UAE, sharks have been impacted by targeted commercial fisheries until 2014 when a ban on export of sharks was imposed (Ministry of Climate Change and Environment). This species continues to be impacted by artisanal and bycatch fisheries (Annual Fisheries Statistical Report for Abu Dhabi Emirate 2001-2018), though catch data are not species specific. Marine habitats in the region have experienced high levels of disturbance and are quickly deteriorating due to major impacts from development activities (Sheppard <em style=""font-variant-ligatures: normal;font-variant-caps: normal;orphans: 2; text-align:start;widows: 2;-webkit-text-stroke-width: 0px;text-decoration-style: initial; text-decoration-color: initial;word-spacing:0px"">et al. 2010).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
329863
Taxon name
Carcharhinus falciformis
(Bibron, 1839)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Carcharhinus falciformis
(Bibron, 1839)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
carcharhinidae
Genus
Carcharhinus
Species
falciformis
Species authority
(Bibron, 1839)
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Silky Shark occurs throughout UAE inshore and offshore waters. Little specific data are available for this species in the UAE. There has been a total ban on fishing for this species in UAE waters since 2019. This species is valued for its meat and fins across the Arabian Sea region. It is one of the dominant species in landings across the Arabian Sea region, and both adults and juveniles are landed. It is apparently highly migratory, and has slow life history characteristics including low fecundity and a low annual rate of population increase. Considering this, the species has a low capacity to recover from even moderate levels of exploitation. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated pelagic tuna longline and purse seine fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. Though data specifically from the UAE are not available, individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. It is inferred that declines reported in the Arabian Sea region are representative of its status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by 20-30% over the past three generation lengths, or about 45 years. It is listed as Near Threatened and nearly meets the thresholds for Vulnerable A2cd.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Silky Shark occurs throughout UAE waters. Elsewhere, it is circumglobally distributed in tropical waters (Last and Stevens 2009).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
The Silky Shark is a circumtropical oceanic and coastal-pelagic species, most often found near the edge of continental and insular shelves at depths of 200 m or more in the epipelagic zone. It is often associated with islands, insular slopes and deepwater reefs preferring warmer waters (about 23'°C) although it also occurs from the surface to a depth of at least 500 m offshore (Last and Stevens 2009). Smaller sharks are often found in coastal nurseries and adults further offshore over deeper water. In pelagic habitats, the Silky Shark is often associated with drifting materials on the surface (Filmalter et al. 2013). Life history parameters of this species vary considerably among regions (Clarke et al. 2015a). The maximum size varies from 229-371 cm total length (TL) with a size at maturity from 180-230 cm TL for males and 180-246 cm TL for females (Clarke et al. 2015). Age at maturity ranges from 5-13 years for males and 6-15 years for females with maximum ages of 8-28.6 years for males and 11-35.8 years for females. The Silky Shark gives birth to live young, averaging 5-7 pups per litter with a range of 2-18 pups per litter (Clarke et al. 2015a). Size at birth ranges from 65-81 cm TL and the gestation period ranges from 9-12 months depending on location and study (Clarke et al. 2015). Anderson and Ahmed (1993) report juveniles of 56-63 cm TL captured off the Maldives. Fecundity increases with increasing size of females, and females give birth every 1-2 years (Clarke et al. 2015). In the eastern Arabian Sea, total length and age at maturity for males is 201-“223 cm (TL) and 10 years, and 224-“231 cm and 11 years for females (Varghese et al. 2016). Generation length is estimated to be 15 years based on the average age of maturity of females as 9 years old and average maximum age of 21 years old (excluding outliers). This is in close agreement with generation length of 16 years in Dulvy et al. (2008).
Threats and conservation measures listed
Threats listed in assessment
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by target (for fins and their valuable meat) and bycatch fisheries that are active elsewhere in its range. Marine habitats in the Arabian Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
329859
Taxon name
Isurus oxyrinchus
Rafinesque, 1810
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Isurus oxyrinchus
Rafinesque, 1810
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
lamniformes
Family
lamnidae
Genus
Isurus
Species
oxyrinchus
Species authority
Rafinesque, 1810
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2d
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
In UAE waters, the Shortfin Mako occurs only in offshore waters of the Sea of Oman. Little is known on the population of this species in UAE waters. It is mostly caught as bycatch in longline, purse seine and drift net fisheries targeting tuna and billfish. Most catches are inadequately recorded and likely underestimated in landings data. There is some evidence of declines in average size of individuals in catches off Oman. It is apparently highly migratory, and has slow life history characteristics including low fecundity and a low annual rate of population increase. Considering this, the species has a low capacity to recover from even moderate levels of exploitation. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net, longline and trawl fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. Though data specifically from the UAE are not available, individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. It is inferred that declines reported in the Arabian Sea region are representative of its status in the UAE. Based on recorded levels of exploitation, it is suspected to have declined by 20-30% over the past three generation lengths, or about 75 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2d.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Shortfin Mako occurs in UAE waters on the Sea of Oman coast. It is excluded from the Arabian Gulf. Globally, it is widespread in temperate and tropical oceanic waters of all oceans from about 50'°N (up to 60'°N in the northeast Atlantic) to 50'°S (Compagno et al. 2005).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
The Shortfin Mako is an offshore littoral and epipelagic species found in tropical and warm-temperate seas to depths of up to 750 m (Compagno 2002, Weigmann 2016). This species reaches a maximum size of about 445 cm total length (TL) (Weigmann 2016). Males reach maturity at about 166-195 cm and females at about 265-280 cm (Pratt and Casey 1983, Stevens 1983, Cliff et al. 1990, Varghese et al. 2017). Age at maturity has been determined in several populations, including New Zealand (7-9 years for males, and 19-21 years for females Bishop et al. (2006)), and the NW Atlantic (eight years for males, and 18 years for females (Natanson et al. 2006)). Longevity has been estimated as 29-32 years (Bishop et al. 2006, Natanson et al. 2006). A study conducted off Brazil reported a longevity of 19-28 years and age at maturity of 7-12 years for females and longevity of 16-23 years and age at maturity of 3-6 years for males (Barreto et al. 2016b).The Shortfin Mako is ovoviviparous and oophagous, but what little is known of its reproductive cycle indicates the gestation period is 15-18 months, with a three year reproductive cycle (Mollet et al. 2002). Litter size is 4-25 pups (possibly up to 30, mostly 10-18), which are about 60-70 cm long at birth (Garrick 1967, Compagno 2001). There are comparatively few records of pregnant females. Among 26 shark species, the Shortfin Mako has an intrinsic rebound potential (a measure of its ability to recover from exploitation) in the mid-range (Smith et al. 1998) with an annual rate of population increase at 0.046 yr<sup>-1</sup>. Cortes (2002) calculated a finite rate of increase (lambda) of 1.141 (1.098 to 1.181 95% CI, r = 0.13) and the average reproductive age as 10.1 (9.2 to 11.1 95% CI) years. Generation length is estimated at 24-25 years based on data for this species from New Zealand and the NW Atlantic (Bishop et al. 2006, Compagno et al. 2005, Natanson et al. 2006).
Threats and conservation measures listed
Threats listed in assessment
In the UAE, sharks have been impacted by targeted commercial fisheries until 2014 when a ban on export of sharks was imposed (Ministry of Climate Change and Environment). Sharks continue to be impacted by artisanal and bycatch fisheries (Annual Fisheries Statistical Report for Abu Dhabi Emirate 2001-2018), though catch data are not species-specific. This species is impacted by bycatch fisheries that are active elsewhere in its range.
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
330724
Taxon name
Acanthodactylus boskianus ssp. asper
(Audouin, 1829)
Infrarank
Acanthodactylus boskianus asper
Infratype
Subspecies (animalia)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Acanthodactylus boskianus ssp. asper
(Audouin, 1829)
Assessed taxon level
Subspecies
Infrarank
Acanthodactylus boskianus asper
Infratype
Subspecies (animalia)
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
lacertidae
Genus
Acanthodactylus
Species
boskianus
Species authority
(Audouin, 1829)
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
B1a+2a
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This subspecies is listed as Near Threatened for the UAE. It has a very limited distribution within the United Arab Emirates on gravel plains bordering the Hajar Mountains on the west from 100 m to 300 m asl. The area of occupancy (AOO) is just 24 km<sup>2</sup>, and the extent of occurrence (EOO) is 195 km<sup>2</sup>. There are no current major threats to the species, however, one known locality is subject to intensive recreational use, and another area faces significant potential impacts from gravel extraction. The species has restricted AOO and EOO, and occurs in fewer than ten locations, however at present, no continuing decline is known. It qualifies as NT under Criterion B (B1 and B2). This taxon is not a non-breeding visitor, and it is presumed that any immigration from populations from Oman is not significant, and therefore there is no adjustment to the Category according to the IUCN regional and national Guidelines (IUCN 2012). Further monitoring and research are required, and the species should be reassessed if new data become available.
Assessment details
Year assessed
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the United Arab Emirates, this subspecies is known from a small area on gravel plains bordering the western side of the Hajar Mountains (Roobas and Feulner 2013, Roobas et al. 2014) from 100 m to 300 m asl (Burriel-Carranza et al. in press). The AOO is just 24 km<sup>2</sup>, and the EOO is 195 km<sup>2</sup>.Globally, the subspecies is very widely distributed and known from Morocco, Algeria, Tunisia, Libya, Egypt, Jordan, Western Sahara, Mauritania, Mali, Nigeria, Sudan, Ethiopia, Eritrea, Chad, Yemen, Saudi Arabia, Oman and Kuwait (Tamar et al. 2014, 2016).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
The subspecies is found on hard desert surfaces such as sandy-gravel plains, dry wadis, interdunal plain and stony outwash plains (Gardner 2013).It is an active, diurnal ground-dwelling animal, with a diet that includes invertebrates and smaller lizards (Gardner 2013). In winter it is active throughout the day, but in summer may have a bimodal activity pattern, or even be active in mornings only when particularly hot. Clutch size is reported to be two to eight, and repeated clutches may be laid (Gardner 2013). The breeding season in the United Arab Emirates is observed to be from at least late summer through mid-winter (Roobas and Feulner 2013, Roobas et al. 2014).
Threats and conservation measures listed
Threats listed in assessment
There are at present no major threats known, however, there is quarrying (gravel extraction) near one known locality, and this has the potential to significantly impact the species in the future. A further locality is subject to intensive recreational use.
Publication
Els, J., Allen, D., Hilton-Taylor, C., Harding, K. (2019). UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles. MOCCAE, UAE
Assessment ID
329990
Taxon name
Acomys dimidiatus
(Cretzschmar, 1826)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Acomys dimidiatus
(Cretzschmar, 1826)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
rodentia
Family
muridae
Genus
Acomys
Species
dimidiatus
Species authority
(Cretzschmar, 1826)
Taxonomic notes and synonyms listed
Formerly considered a subspecies of Acomys cahirinus. See Musser and Carleton (2005) for details concerning the relationship between Acomys dimidiatus and A. cahirinus.
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Near threatened
Abbreviated status
NT
Qualifying criteria (if given)
B1b(iii)
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Within the UAE, this species is restricted to rocky areas, primarily the Hajar Mountains, Jebel Hafeet and Qarn Nazwa. The extent of occurrence (EOO) is just over 6,000 km<sup>2</sup>, there is a continuing decline in the extent and quality of habitat due to a variety of threats, however, the number of locations is more than ten and the range is not severely fragmented, so it is assessed as Near Threatened (close to qualifying for a threatened category under criterion B1ab(iii)). There might be some rescue effect from populations in adjoining countries, particularly Oman, but this is not thought to be significant hence the regional assessment is not adjusted.
Assessment details
Year assessed
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species was first recorded for the UAE in 1971 at Jebel Faiyah, Sharjah, and then again in 1991 when a dead specimen was found by a road near Ghayl, Ra's al Khaimah. Subsequent surveys have shown that this species is quite widespread and numerous through the Hajar Mountains at lower elevations, particularly where Acacia tortilis is present. The species is also found on Jebel Hafeet, where it occurs at all elevations including barren rocks near the summit (Aspinall et al. 2005). It has also been recorded at several sites in Ras Al Khaimah (RAK Nature pers. comm. 2018) and on Qarn Nazwa in Dubai Emirate. Globally, this species is distributed from the Sinai Peninsula of Egypt through much of the Arabian Peninsula to Iran and southern Pakistan (Cassola 2016a).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
Predominantly crepuscular and nocturnal and prefers all kinds of rocky habitats (Harrison and Bates 1991). Found on boulder-strewn slopes and rocky terrain where it lives in crevices among boulders (Cunningham 2008) and in wadi beds in Wadi Wurayah (Judas 2016). In a community structure study of Jebel Al Jais in Ras Al Khaimah Emirate, the species was recorded at elevations ranging from 450-“1,650 m, was most abundant in the wadi area around 450 m, and its abundance declined with increasing altitude (Melville and Chaber 2016). It was trapped at around 180 m asl on he outlying hill of Jebel Nazwa (Qarn Nazwa) in 2018 (J. Judas pers. comm. 2018). This species is omnivorous (Melville and Chaber 2016). There is evidence from trapping surveys that the Arabian Spiny Mouse is more susceptible than other small mammal species to disturbance and fragmentation (B. Howarth pers. comm. 2018).
Threats and conservation measures listed
Threats listed in assessment
Overgazing, quarrying, road construction and other development activities in the mountains result in habitat loss and degradation and increased fragmentation. Species in the mountains may also be affected indirectly by falling water tables due to over-abstraction and reduced precipitation. An increase in numbers of feral cats and Red Foxes may also pose a threat to all small mammals.
History
The backcasted 1996 assessment for this species is Near Threatened (almost meets a threatened listing under criterion B1ab(iii)) which matches the listing given by Hornby (1996).
Publication
Mallon, D., Hilton-Taylor, C., Allen, D., & Harding, K. (2019). UAE National Red List of Mammals: Marine and Terrestrial. A report to the Ministry of Climate Change and Environment, United Arab Emirates (p. 41). IUCN Global Species Programme. https://bit.ly/2RdZCQR