Fantail Stingray
Fantail Stingray
Dangerous© iamsiggi
Fishes · Rays · Whiptail stingray

Fantail Stingray

Pastinachus sephen (Forsskål, 1775)
syn. Dasyatis gruveli, Dasyatis sephen, Dasybatus gruveli, Dasybatus sephen, Hypolophus sephen, Pastinachus gruveli +6 more
1.8 m (3 m)250 Kg1-60 mDangerousVenomousNear Threatened
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The cowtail stingray (Pastinachus sephen) is a notable species within the family Dasyatidae, known for its extensive distribution across the Indo-Pacific region and its occasional presence in freshwater environments. Commonly referred to as the banana-tail ray, drab stingray, fantail ray, feathertail stingray, or frill-tailed stingray, this species is sometimes classified under the genera Dasyatis or Hypolophus—an outdated synonym for Pastinachus. The most distinguishing feature of the cowtail stingray is the prominent, flag-like ventral fold on its tail, which becomes particularly noticeable when the ray is in motion. The species is currently facing significant threats due to overfishing, primarily for its high-quality shagreen, a type of leather.

Geographically widespread, the cowtail stingray inhabits the tropical waters of the Indo-Pacific, stretching from 🇿🇦 South Africa and the 🌊 Red Sea to 🇯🇵 Japan and 🇦🇺 Australia, including areas like Melanesia and 🇫🇲 Micronesia. This amphidromous ray is known to migrate into estuaries and rivers, with reports documenting its presence in freshwater habitats across Southeast Asia, including a notable occurrence in the Ganges River approximately 2,200 km from the sea. Predominantly found on sandy substrates in coastal waters and coral reefs, the cowtail stingray can inhabit depths of up to 60 meters.

Morphologically, the cowtail stingray is characterized by a thick pectoral fin disk with near-straight anterior margins and rounded apices, measuring 1.1–1.3 times as long as it is wide. Its broadly rounded and blunt snout, diminutive and widely spaced eyes, and narrow mouth—equipped with 20 rows of distinctive high-crowned, hexagonal teeth and five papillae on the mouth floor—further define its anatomy. The broad-based tail, ending in a filamentous tip and hosting a single venomous spine positioned posteriorly to the pelvic fins, lacks an upper tail fold. The high ventral tail fold, which is two to three times the height of the tail, does not extend to the tip. The cowtail stingray's dorsal surface, except the extremities of the disk, is adorned with fine dermal denticles. Juveniles display four circular tubercles centrally located on the disk, which often become indistinct with maturity. Coloration is uniformly grayish-brown to black above and predominantly white below, with the tail fold and tip being black. They can grow up to 3 meters in length, 1.8 meters across, and weigh up to 250 kg.

Ecologically, cowtail stingrays are solitary predators, preying on bony fishes, crustaceans, polychaete worms, sipunculids, and molluscs. In turn, they are preyed upon by various shark species and the Indo-Pacific bottlenose dolphin (Tursiops aduncus). When threatened, these stingrays exhibit a flight response at a 45° angle to evade predators effectively while maintaining awareness of their presence.

Reproductively, cowtail stingrays are ovoviviparous, with embryos nourished in later stages of development by maternal histotroph. Females give birth to live young measuring at least 18 centimeters across. Parasitically, they are known hosts to Dendromonocotyle ardea, Decacotyle tetrakordyle, and Pterobdella amara.

Behavioral observations in Shark Bay, 🇦🇺 Australia, reveal that cowtail stingrays utilize shallow sandy flats for resting during high tide, often forming small groups for protection. Such groupings likely serve as a defense mechanism against predators, allowing them to maintain visual coverage in all directions. Additionally, these rays form mixed-species assemblages with reticulate whiprays (Himantura uarnak), potentially benefiting from their enhanced predator detection capabilities.

Despite their ecological and commercial significance, the cowtail stingray is vulnerable to unsustainable harvesting practices. The increased demand for shagreen since the 1990s, utilized in various fashion accessories, poses a severe threat to their populations due to their slow reproductive rates and longevity. Without regulation, continued exploitation could lead to a precipitous decline in their numbers.

Why it's threatened

Residential & commercial development
Housing & urban areas
Biological resource use
Unintentional effects: (subsistence/small scale) [harvest] · Unintentional effects: (large scale) [harvest]

Cowtail Rays are regularly captured in trawl, gillnet and longline fisheries across the range of this species. In places, fishing pressure is intense and increasing. For example, in the Indian state of Gujarat, the number of trawlers increased from ~6,600 in 2004 to over 11,500 trawlers in 2010 (Zynudheen et al. 2004, CMFRI 2010). Similarly, gillnet fishing (including net length) is increasing in India (Bineesh K.K., unpub. data). Indian west coast annual landings of Cowtail Rays have fluctuated between ~14 and 40 tonnes in recent years (Bineesh K.K. pers. comm. 06/02/2017). In Pakistan waters, about 2,000 trawlers operate in shelf waters, targeting shrimp in shallow waters and fish in deeper shelf waters (M. Khan pers. comm. 06/02/2017). In Iran, there is increasing fishing effort with the number of fishermen going from 70,729 in 1993 to 109,601 in 2002 (Valinassab et al. 2006). In the Saudi Red Sea, the number of traditional vessels operating increased from about 3,100 to 10,000 between 1988 and 2006 (Bruckner et al. 2011).

Cowtail Rays are generally discarded in the Red Sea and the Gulf (due to undesirable meat), in contrast to the normal retention in India. Fishers will often remove the tail before release. Rays without tails seem to survive as these have been recorded on BRUVs in the region (J. Spaet unpub. data). Survivorship from released line catches would be higher than trawl where the species may suffer mortality even if released.

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) which is likely to impact this species.

Threat classification from the IUCN Red List.

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Last Update: June 28, 2026