Halavi Guitarfish
© Andy Murch
Fishes · Rays · Guitarfish

Halavi Guitarfish

Glaucostegus halavi (Forsskål, 1775)
syn. Raia halavi, Raja halavi, Rhinobatos (Scobatus) halavi, Rhinobatos halavi, Rhinobatus halavi, Scobatus halavi
171 cm1-100 mCITES IICritically Endangered
874

The Halavi Guitarfish (Glaucostegus halavi), belonging to the Glaucostegidae family, is a species of ray native to the Indo-West Pacific, spanning from the 🌊 Red Sea to the 🌊 Gulf of Oman. There are unconfirmed occurrences east of 🇴🇲 Oman, with documented appearances in the Levantine waters in 1997 and 2004, leaving its potential establishment in the Mediterranean Sea uncertain. Its nomenclature, "halavi," is derived from the Arabic word حلاوي (halawi).

Morphologically, the Halavi Guitarfish is characterized by a large size and distinctive features, such as a wide, short, and pointed snout with a rounded tip. The rostral ridges are conjoined along most of the snout length, and the rostral cartilage exhibits a sharply defined posterior margin. It has small eyes with a snout length measuring 6.3–7.8 times the orbit length. The spiracles are distinguished by two short, widely spaced skin folds, and the nasal flaps extend marginally beyond the nostril opening. The disc's anterior margins are straight or slightly convex, with broadly rounded pectoral apices. The skin, covered in small denticles, has a rough texture along the rostral ridge, between the eyes, on the shoulders, and along the centerline. Notably, small thorns are located around the eyes, with a single larger thorn on each shoulder and a continuous row along the medial ridge from nape to tail.

The tail is robust and slightly exceeds the disc length. The dorsal fins are large, well-separated, with narrowly rounded apices, while the caudal fin is triangular and lacks a defined lower caudal lobe. The dorsal coloration ranges from yellowish to greyish-brown, unmarked, with pale rostral cartilage, while the ventral side is white.

The species reaches a maximum length of 171 cm, with newborns measuring approximately 29 cm. It inhabits tropical seas, favoring benthic sandy substrates and seagrass environments, from very shallow waters to depths of at least 100 meters, particularly in the Northundefined, from 🇰🇪 Kenya to 🇮🇳 India, including the Arabian Sea and 🌊 Red Sea.

In terms of reproduction, the Halavi Guitarfish is aplacental viviparous, with a litter size of approximately 10. Its diet primarily consists of benthic invertebrates. Behavioral observations note that it ventures into very shallow waters for feeding, with its reproductive season in the 🌊 Red Sea occurring from May to October. Generally, it is skittish in the presence of divers.

From a diving perspective, the Halavi Guitarfish is encountered with relative frequency by divers and snorkelers in the 🌊 Red Sea, notably at Gorgonia Beach off Marsa Alam, 🇪🇬 Egypt.

Conservation Status: Critically Endangered

The Halavi Guitarfish occupies a limited range within a region subjected to intensive fishing practices in the 🌊 Indian Ocean and Gulf of Arabia. It is both a retained component of bycatch and a directly targeted species, leading to significant population declines. In particular, reports from the 🇦🇪 United Arab Emirates indicate an 80% reduction in population over the last 30 years.

Why it's threatened

Biological resource use
Intentional use: (subsistence/small scale) [harvest] · Intentional use: (large scale) [harvest] · Unintentional effects: (subsistence/small scale) [harvest] · Unintentional effects: (large scale) [harvest]

Globally, giant guitarfishes are subject to intense fishing pressure on their coastal and shelf habitats that is unregulated across the majority of their distributions. Giant guitarfishes are captured in industrial, artisanal, and subsistence fisheries with multiple fishing gears, including gillnet, trawl, hook and line, trap, and seine net and are generally retained for their meat and fins (Bonfil and Abdallah 2004, White and Sommerville 2010, Moore 2017, Jabado 2018). There is a high level of fisheries resource use and increasing fishing pressure across the range of the Halavi Guitarfish, and demersal coastal fisheries resources have been severely depleted in significant areas of the Indo-West Pacific, including India (Mohamed and Veena 2016).

In general, fishing effort and the number of fishers has increased in recent decades across the range of this species, with demand for shark and ray product increasing over the same period due to the shark fin trade (Chen 1996, Jabado et al. 2017). In the Red Sea for example, the number of traditional boats tripled from 3,100 to 10,000 from 1988 to 2006 (Bruckner et al. 2011), and in the Indian state of Gujarat, the number of trawlers increased from about 6,600 in the early 2000s to 11,582 in 2010 (Zynudheen et al. 2004, CMFRI 2010, Jabado et al. 2017). Most countries have significant fishing fleets operating in coastal waters e.g. Oman (19,000 artisanal boats) and Pakistan (2,000 trawlers) (Jabado et al. 2017).

Sharks and rays, including giant guitarfishes, are often targeted and now heavily exploited across the region by net and trawl fisheries and increasing fishing effort has put significant pressure on all giant guitarfish species in the Indo-West Pacific. Furthermore, the high value of fins is driving retention and trade of giant guitarfishes globally (Moore 2017, Jabado 2018). The Halavi Guitarfish is landed throughout its range (e.g. Spaet and Berumen 2015, Henderson et al. 2007, Jabado 2018) and several countries within the distribution of this species rank among the top 20 shark fishing nations globally, specifically India, Pakistan, and Iran (Lack and Sant 2011).

The shallow, inshore soft-bottom habitat preferred by the species is threatened by habitat loss and environmental degradation (White and Sommerville 2010, Moore et al. 2012, Jabado et al. 2017, Moore 2017). In the Arabian Sea and adjacent waters, dredging and coastal land reclamation has increased in recent years and has resulted in almost total loss of mangroves in some areas, such as Bahrain (Sheppard et al. 2010, Jabado et al. 2017).

Threat classification from the IUCN Red List.

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Last Update: June 28, 2026