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Overview

Brief Summary

Syngnathoides biaculeatus, the Alligator Pipefish, is a member of the family Syngnathidae (along with the pipefishes, this family includes the seahorses and sea dragons). Alligator Pipefish are found in shallow coastal waters, living among seagrasses, where they feed on small crustaceans and fish (Nakamura et al. 2003). Alligator Pipefish grow to around 280 mm total length. The Alligator Pipefish is thought to be the most heavily exploited pipefish in traditional Chinese medicine. (Barrows et al. 2008 and references therein)

As is the case for the males of all pipefishes and seahorses, male Alligator Pipefish incubate the eggs before they hatch. Eggs are protected in male brood pouches until they have fully developed and hatch as juveniles. In this species, males have a simple "pouch" morphology in which the embryos are attached to the ventral surface of the male abdomen, which has no flaps of surrounding tissue. Initial clutch size is directly correlated to the size of the male carrying the eggs. Reproduction occurs year-round and generation time is short. (Barrows et al. 2008 and references therein).

The Alligator Pipefish has a wide geographic range, being found in seagrass habitats from the northern Red Sea and the eastern coast of Africa eastward to Japan, Samoa, the Tonga Islands, and Australasia (Dawson 1985, cited in Barrows et al. 2008).

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Comprehensive Description

Biology

Occur in protected coastal shallows over or among algae, seagrasses (Ref. 41878), or floating weeds (Ref. 1602). Juveniles occasionally found near the surface (Ref. 4281). Ovoviviparous (Ref. 205). The males carry the eggs in a brood pouch which is found under the tail (Ref. 205). Used in Chinese medicine to extract Hailong, one of the important drugs (Ref. 12206). Has been reared in captivity (Ref. 35416).
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Distribution

Range Description

Syngnathoides biaculeatus has a wide geographic range. It has been recorded in surveys and taxonomic overviews from the Red Sea and the African east coast to Knysna, South Africa (Dawson 1985, Dawson 1986). It is also found in the Indo-Pacific from the east coast of India, throughout the South China Sea and has been recorded as far northward as northern Japan. It has been found in three states and one territory in Australia: Western Australia, the Northern Territory, Queensland, and New South Wales (Paxton et al. 1989). It has been recorded near the islands of Micronesia and Samoa (Randall et al. 1997).

Australian Marine Protected Areas in Which Has Been Recorded (Pogonoski et al. 2002): In Australia, S. biaculeatus is found in the following marine protected areas: Ashmore Reef National Nature Reserve, off northern Western Australia, Cartier Island Marine Protected Area, Great Barrier Reef Marine Park, Queensland, and CoburgMarinePark, in the Northern Territory (Pogonoski et al. 2002).

Museum Records Worldwide: in Australia, there are 106 specimens (standard length 100-288 mm), collected from a depth range of 0 to 5 m, ranging in geographical distribution from the Timor Sea, Northern Territory south-eastwards to Batemans Bay (35°44’S), New South Wales on the east coast of Australia, and from Ashmore Reef (12°13’S) southwards to Geraldton (28°46’S) on the west coast of Australia. Outside Australia there are specimens from the Andaman Islands, India, Malay Archipelago, Guam, Papua New Guinea and the Solomon Islands. Specimens were collected between circa 1879 and 1998 (Pogonoski et al. 2002).

Other museum records are available from FishBase and the Ocean Biogeographic Information System (OBIS) and include specimens collected from Suva Harbor in Fiji, Singapore, Kenya, and Yemen (Froese and Pauly 2007, Ocean Biogeographic Information System 2007). Specimens listed in Fishbase/OBIS have collection dates from 1828 to 2004.
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Indo-Pacific: Red Sea and Knysna, South Africa (Ref. 4281) to Samoa, north to southern Japan, south to New South Wales.
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Red Sea, Indo-West Pacific: East Africa, South Africa, Madagascar and Mauritius (Mascarenes) east to Marshall Islands and Samoa, north to southern Japan, south to Western Australia, New South Wales (Australia), New Caledonia and Tonga.
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Physical Description

Morphology

Dorsal spines (total): 0; Dorsal soft rays (total): 38 - 48; Analspines: 0; Analsoft rays: 4
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Size

Maximum size: 290 mm TL
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Max. size

29.0 cm TL (male/unsexed; (Ref. 4281))
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Diagnostic Description

Description

Occurs in protected coastal shallows over or among algae, seagrasses, or floating weeds (Ref. 1602). Juveniles occasionally found near the surface (Ref. 4281).
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Variable green to brown or grey, depending on habitat (Ref. 48635).Description: Characterized by variable white and dark markings on body; absence of caudal fin; rings 15-18 + 40-54; continuous superior and inferior trunk ridge with respective tail ridges; inconspicuous inferior trunk ridge; dorsally deflected lateral trunk ridge behind anal ring, ends below superior tail ridge near rear base of dorsal fin; length of snout 1.7-1.8 in head length; depth of snout 5.3-7.8 in snout length; head length 4.9-6.3 in SL (Ref 90102).
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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology

Habitat

Syngnathoides biaculeatus is generally found in seagrass beds or algal flats in the protected shallow waters of lagoons and bays, its colouring matching plants well (Randall et al. 1997). Adults are found in large Sargassum rafts (Kuiter 1996) and juveniles are occasionally found among debris floating offshore (Dawson 1985). In Queensland, Australia, this species is found in estuaries, usually in association with Zostera seagrass, to which it anchors itself by means of its prehensile tail (Grant 1978).

Behaviour and Biology

Syngnathoides biaculeatus has a breeding season of between October and April in Moreton Bay, Australia (Takahashi et al. 2003) but year-round in BootlessBay, PNG (Barrows et al. unpub). Males mature and can begin brooding at a length of about 180 mm (Dawson, 1985; Takahashi et al. 2003) although smaller mature males have been observed (Barrows et al., unpub). Brood size for males was comparable to that of other syngnathids, at 60-200 eggs (Takahashi et al. 2003) although ongoing research suggests that larger broods can occur (Barrows et al., unpub). The eggs can vary in colour (they can be clear, white, brown, or green) as they develop and are carried on the abdomen of the male until they hatch (Grant 1978, Takahashi 2000).

Syngnathoides biaculeatus is a poor swimmer, propelling itself by the winnowing action of the dorsal and pectoral fins (Pogonoski et al. 2002). Some individuals have been observed near the surface of the water or jumping out of the water entirely (Dawson 1986, Kuiter 1996). Prey items include shrimps, fish, and amphipods (Nakamura et al. 2003) as well as other tiny crustaceans (Allen and Swainston 1992).

Size

Syngnathoides biaculeatus has been reported to achieve a maximum length of between 260 to 300 mm (Kuiter 1996, Takahashi et al. 2003) and displays significant size dimorphism, with males growing bigger than females (Takahashi et al. 2003). Although growth of S. biaculeatus has been reported as rapid over a life span of less than two years (Takahashi et al. 2003), more recent studies suggest that growth rates are slower and life spans can reach three years (Barrows et al. unpub data).


Systems
  • Marine
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Environment

reef-associated; non-migratory; marine; depth range 0 - 10 m (Ref. 90102)
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Depth range based on 15 specimens in 1 taxon.
Water temperature and chemistry ranges based on 7 samples.

Environmental ranges
  Depth range (m): 0.915 - 475
  Temperature range (°C): 28.408 - 28.954
  Nitrate (umol/L): 0.050 - 0.617
  Salinity (PPS): 33.821 - 34.438
  Oxygen (ml/l): 4.450 - 4.545
  Phosphate (umol/l): 0.072 - 0.160
  Silicate (umol/l): 1.103 - 1.900

Graphical representation

Depth range (m): 0.915 - 475

Temperature range (°C): 28.408 - 28.954

Nitrate (umol/L): 0.050 - 0.617

Salinity (PPS): 33.821 - 34.438

Oxygen (ml/l): 4.450 - 4.545

Phosphate (umol/l): 0.072 - 0.160

Silicate (umol/l): 1.103 - 1.900
 
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Trophic Strategy

Occur in protected coastal shallows over or among algae, seagrasses, or floating weeds (Ref. 1602). Juveniles occasionally found near the surface (Ref. 4281). Feed on benthic invertebrates and zooplankton (Ref. 11889).
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Life History and Behavior

Life Cycle

Male carries the eggs in a brood pouch (Ref. 205).
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Molecular Biology and Genetics

Molecular Biology

Barcode data: Syngnathoides biaculeatus

The following is a representative barcode sequence, the centroid of all available sequences for this species.


There are 2 barcode sequences available from BOLD and GenBank.

Below is a sequence of the barcode region Cytochrome oxidase subunit 1 (COI or COX1) from a member of the species.

See the BOLD taxonomy browser for more complete information about this specimen and other sequences.

CCTTTATTTAGTATTTGGTGCATGAGCTGGAATAGTCGGGACCGCCCTAAGCCTACTTATCCGAGCAGAGCTAAGCCAACCCGGGGCCCTACTAGGGGATGATCAGATTTATAATGTAATTGTCACCGCCCATGCATTCGTCATAATTTTCTTTATAGTTATACCAATCATGATTGGCGGCTTTGGTAATTGGTTAGTTCCACTAATAATTGGGGCACCCGATATAGCCTTTCCCCGAATAAACAATATAAGCTTCTGGCTTCTTCCGCCCTCTTTTCTTCTTCTCCTTGCCTCATCTGGGGNTGAAGCAGGAGCAGGCACCGGATGAACTGTTTATCCACCCCTTGCAGGTAACCTCGCCCATGCAGGAGCATCAGTAGACCTTACTATTTTCTCCCTTCACTTAGCAGGAGTTTCCTCAATCCTAGGGGCAATTAACTTCATCACCACTATTATTAACATAAAACCACCCTCTATTTCCCAATACCAAACACCCTTGTTCGTCTGAGCCGTCCTAATTACTGCTGTCCTCCTTCTATTGTCACTCCCAGTTTTGGCAGCCGGCATTACAATACTCCTCACAGACCGCAACCTTAATACAACCTTTTTTGACCCTGCCGGAGGGGGTGACCCAATTCTTTACCAACACCTG
-- end --

Download FASTA File

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Statistics of barcoding coverage: Syngnathoides biaculeatus

Barcode of Life Data Systems (BOLDS) Stats
Public Records: 3
Specimens with Barcodes: 8
Species With Barcodes: 1
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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2008

Assessor/s
Bartnik, S., Morgan, Pogonoski, J., Pollard, D. & Paxton, J.

Reviewer/s
Martin-Smith, K. & Caldwell, I. (Syngnathid Red List Authority)

Contributor/s

Justification
This species meets the criteria for a Data Deficient listing. The information available for Syngnathoides biaculeatus includes distribution and life history parameters such as growth, reproduction, and development data (Takahashi et al. 2003, Dhanya et al. 2005) but excludes data on population dynamics. Syngnathoides biaculeatus is a syngnathid that has a long history of use in traditional medicine (Shi et al. 1993, Pogonoski et al. 2002). While there is abundant information on the occurrence of this species, information on catch and trade levels is scarce. A listing of Data Deficient does not imply that the taxon is not threatened but that not enough information exists to quantify or even estimate extinction risk. Application of the category Data Deficient is a call for more research and scrutiny to be directed at this species. Until there exists more information on the main exploitation method for S. biaculeatus, (as it is not known if there are directed fisheries for the species or if individuals are caught only as bycatch), the distribution of any fisheries, and the volume of individuals that are caught and traded, the impact of the trade for traditional medicines cannot be assessed with rigour.

History
  • 1996
    Data Deficient
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Population

Population

While S. biaculeatus has been reported by many authors in its range, there is no information available to our knowledge about population structure or sizes. Takahashi et al. (2003) (and earlier thesis Takahashi 2000) report on index of population size (CPUE) and seasonal changes in Moreton Bay, Queensland. Work in Bootless Bay, PNG (Barrows, Baine and Martin-Smith unpub. data) shows they are very common (found at all seagrass sites) in moderate abundance (2-6 individuals/100 m²) with no systematic changes across the year.


Population Trend
Unknown
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Threats

Major Threats

This species has a history of use in the Chinese traditional medicine trade. Known as Hailong (Shi et al. 1993), it has been observed for sale in traditional medicine stores in Sydney, Australia (C. Woodfield, pers. comm., Martin-Smith and Vincent 2006). The origins of the specimens that enter the medicine trade have not been established, although it is likely there are from wild populations as S. biaculeatus rearing in aquaculture facilities has not been reported. Live specimens are also sold as pets for home aquariums and this trade could threaten wild populations if individuals are being removed from the wild to fulfill the home aquarium industry demand (S. Bartnik, pers. obs).

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Data deficient (DD)
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Management

Conservation Actions

Conservation Actions
This species has been identified or protected by the following conservation actions.
  • In Australia all syngnathids became subject to the export controls of the Commonwealth Wildlife Protection (Regulation of Exports and Imports) Act 1982 on 1 January 1998 (Pogonoski et al. 2002).
  • In Australia, all syngnathids and solenostomids are listed as marine species under section 248 of the Environment Protection and Biodiversity Conservation (EPBC) Act 1999 (Pogonoski et al. 2002).
  • This species is listed as Data Deficient by the Australian Society for Fish Biology (ASFB) in its 2001 Conservation Status of Australian Fishes document, the most recent AFSB listing available (ASFB 2007).
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Relevance to Humans and Ecosystems

Benefits

Importance

aquarium: public aquariums
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Wikipedia

Alligator pipefish

The alligator pipefish or double-ended pipefish (Syngnathoides biaculeatus) is a species of fish in the family Syngnathidae and is the only species in the monotypic genus Syngnathoides. It is found in shallow water in the tropical and subtropical Indo-Pacific, its range extending from East Africa to northern Australia. This fish lives in habitats of seagrass and seaweed, and hides by positioning itself vertically with its head down amidst the similar-coloured fronds of vegetation. The elongated, well-camouflaged body can reach 29 cm (11 in) in length. It feeds by sucking up its prey.

Description[edit]

The alligator pipefish can grow to a length of about 29 cm (11 in) though a more typical length is 20 cm (8 in). The narrow head has the snout tipped by a pair of short tentacles and the body is elongated and cylindrical. The dorsal fin has 38 to 48 soft rays and the anal fins have 4 soft rays. The tail is long and tapering. It is prehensile and lacks a tail fin, being used to anchor the fish to vegetation. The colour of this fish tends to match its surroundings and is usually some shade of green, brown or grey. Females are often blotched and may have a dark zigzag line running along the abdomen.[3][4][5]

Distribution and habitat[edit]

The alligator pipefish occurs in tropical and subtropical parts of the Indian Ocean and Pacific Ocean. Its range extends from South Africa, the East Coast of Africa and the Red Sea to India, Japan, Indonesia, the Philippines, New Guinea, Australia and various Pacific Islands. In Australia its range extends from Geraldton in Western Australia around the coast of the Northern Territory and Queensland to Batemans Bay in New South Wales. It occurs in lagoons and on reef flats, in bays and estuaries, in seagrass meadows and in floating masses of algae, usually at depths of less than 5 m (16 ft).[1]

Behaviour[edit]

The alligator pipefish is an inefficient swimmer, moving by an undulating motion of its pectoral and dorsal fins.[1] It feeds on zooplankton and small creatures which it sucks into its mouth. The diet includes amphipods, mysids, shrimps, other benthic invertebrates and small fish.[3]

The alligator pipefish is sexually dimorphic with males being larger than females. Males become mature at a length of about 180 mm (7 in). Breeding takes place during the summer in Moreton Bay, Queensland but occurs at any time of year in Papua New Guinea. A female produces a batch of 60 to 200 eggs which are retained by the male in a brood pouch on his abdomen.[5] Here they remain until they hatch. The male and female seem to have a monogamous relationship with all the developing eggs being at the same stage of development and presumably the product of a single female.[5]

Status[edit]

The alligator pipefish is dried and used in traditional Chinese medicine when it is known as "hailong". This fish appears in the pet trade for sale to home aquarium owners and is also kept and reared in public aquariums. No studies on the population trend for this species have been done and the International Union for Conservation of Nature does not know where the traded fish are acquired; it is unclear whether these are wild-caught fish, whether there are dedicated fisheries for this species, whether the fish are caught as bycatch or whether they are captive-reared. For these reasons, the IUCN considers it has insufficient information to assess the conservation status of this fish and has therefore listed it as being "data deficient".[1]

References[edit]

  1. ^ a b c d Bartnik, S.; Morgan,; Pogonoski, J.; Pollard, D.; Paxton, J. (2008). "Syngnathoides biaculeatus". IUCN Red List of Threatened Species. Version 2014.2. International Union for Conservation of Nature. Retrieved 2014-10-29. 
  2. ^ a b Bailly, Nicolas (2013). "Syngnathoides biaculeatus (Bloch, 1785)". World Register of Marine Species. Retrieved 2014-10-29. 
  3. ^ a b Froese, R. and D. Pauly. Editors. (2011). "Syngnathoides biaculeatus (Bloch, 1785)". FishBase. Retrieved 2014-10-30. 
  4. ^ "Alligator pipefish: Syngnathoides biaculeatus". Wild factsheets. Wild Singapore. Retrieved 2014-10-30. 
  5. ^ a b c Takahashi, Eri; Connolly, Rod M.; Lee, S.Y. (2003). "Growth and Reproduction of Double-Ended Pipefish, Syngnathoides biaculeatus, in Moreton Bay, Queensland, Australia". Environmental Biology of Fishes 67 (1): 23–33. doi:10.1023/A:1024416031274. 
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