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Syngnathus watermeyeri

Status_ne_offStatus_dd_offStatus_lc_offStatus_nt_offStatus_vu_offStatus_en_offStatus_cr_onStatus_ew_offStatus_ex_off

Taxonomy [top]

Kingdom Phylum Class Order Family
ANIMALIA CHORDATA ACTINOPTERYGII SYNGNATHIFORMES SYNGNATHIDAE

Scientific Name: Syngnathus watermeyeri
Species Authority: Smith, 1963
Common Name(s):
English Estuarine Pipefish, River Pipefish
Synonym(s):
Syngnathus watermayeri Smith, 1963 [orth. error]

Assessment Information [top]

Red List Category & Criteria: Critically Endangered B1ab(i,ii,iii); C2a(i) ver 3.1
Year Published: 1996
Date Assessed: 2009-12-15
Assessor(s): Sorensen, M. & Bills, R.
Reviewer(s): Curtis, J. & O’Donnell, K.
Justification:

S. watermeyeri has been listed as Critically Endangered due to its restricted extent of occurrence, continued decline in habitat quality, and the absence of mature individuals in the latest intensive surveys.

Until a programme is in place that regulates fresh water pulses into South African estuaries, which are needed to maintain the S. watermeyeri food supply, it will remain Critically Endangered.

History:
1996 Critically Endangered (Baillie and Groombridge 1996)
1996 Critically Endangered
1996 Critically Endangered
1994 Extinct (Groombridge 1994)
1990 Vulnerable (IUCN 1990)
1988 Vulnerable (IUCN Conservation Monitoring Centre 1988)

Geographic Range [top]

Range Description:

S. watermeyeri is known only from the Bushmans, Kariega, and Kasouga estuaries on the Eastern Cape coast of South Africa (Whitfield 1995, Cowley 1998, Vorwerk et al. 2007).

Countries:
Native:
South Africa (Eastern Cape Province)
FAO Marine Fishing Areas:
Native:
Atlantic – southeast; Indian Ocean – western
Range Map: Click here to open the map viewer and explore range.

Population [top]

Population:

Syngnathus watermeyeri has been recorded in small numbers and its presence/absence in surveys has fluctuated dramatically since these surveys began. Initial surveys in 1963 found 10 River Pipefish in the Bushmans estuary, 11 in the Kariega estuary and two in the Kasouga estuary (Whitfield 1995). Between 1989 and 1992, intensive surveys were conducted in all three estuaries with no specimens recorded. As a result, S. watermeyeri was listed as officially Extinct in the 1994 IUCN Red List but in 1996 a new breeding population was discovered in the East Kleinemonde estuary (Cowley 1998). This new population, however, was declared locally extinct in 2003 when a large flood was thought to have washed their preferred eelgrass habitat out to sea, no specimens have since been found in the East Kleinemonde (James et al. 2008).

The most recent surveys occurred in 2006 and found juvenile S. watermeyeri once again in its historic range (Bushmans, Kariega and Kasouga estuaries) where it had not been reported for over four decades (Whitfield and Bruton 1996). These intensive surveys found a total of 20 juvenile specimens in the Kariega estuary, ranging from 0.05 to 0.2 individuals per square metre (Vorwerk et al. 2007). No mature individuals were found. Peaks in abundance were found in areas where mesohaline conditions prevailed and the percentage vegetation cover exceeded 80% (Vorwerk et al. 2007).

Population Trend: Decreasing

Habitat and Ecology [top]

Habitat and Ecology: Reproduction
The male carries the eggs in a brood pouch which is found under the tail (Breder and Rosen 1966). Sexual maturity is attained at approximately 10 cm standard length with males retaining up to 44 embryos. Reproductively active specimens were collected in the Kariega estuary during late September (Whitfield 1995). The life cycle is completed within the estuary.

Habitat

S. watermeyeri occurs in brackish, tidal areas of rivers and is found primarily in association with the eelgrass Zostera capensis and Ruppia cirrhosa, where it feeds almost exclusively on zooplankton (Whitfield 1995).
Systems: Freshwater; Marine

Threats [top]

Major Threat(s):

Syngnathus watermeyeri relies on freshwater pulses which provide the nutrients that enable phytoplankton development and, together with particulate organic material brought down by the rivers, support the zooplankton community upon which these pipefish depend for food. The construction of dams and other impoundments have caused a deprivation of fresh water pulses and a subsequent decline in food supply (Whitfield 1995). Dry conditions in the last few years have caused the Kariega river to stop flowing, which will likely result in the absence of S. watermeyeri in this system once again (A.K.Whitfield pers. comm.).
 
This species may also be particularly susceptible to hypersaline conditions and to large flood events (Vorwerk et al. 2007). A flood event in the East Kleinemonde estuary in 1996 (Cowley 1998) resulted in the apparent localized extinction of S. watermeyeri. This was thought to be the result of primary S. watermeyeri habitat, submerged eelgrass beds, being flushed out to sea (Vorwerk et al. 2007).

Conservation Actions [top]

Conservation Actions:

The South African National Water Act 1998 (Act 36) requires that all rivers should have an Ecological Reserve amount set aside. The Ecological Reserve relates to "the water required to protect the aquatic ecosystems of the water resource", including both rivers and estuaries (Vorwerk et al. 2008a).  Ecological reserves have been determined for some systems in South Africa but not for any estuaries inhabited by S. watermeyeri. When dams were built on the Kariega and its tributary rivers, a water release policy was issued for downstream agriculture but the environmental requirements of estuaries and rivers were not included (Vorwerk et al. 2008a).

Bibliography [top]

Baillie, J. and Groombridge, B. (eds). 1996. 1996 IUCN Red List of Threatened Animals. IUCN, Gland, Switzerland and Cambridge, UK.

Breder, C.M. and Rosen, D.E. 1966. Modes of reproduction in fishes. T.F.H. Publications, Neptune City, New Jersey, USA.

Cowley, P.D. 1998. Fish population dynamics in a temporarily open/closed South African estuary. Rhodes University.

Cowley, P.D., Whitfield A.K. 2001. Ichthyofaunal characteristics of a typical temporarily open/closed estuary on the southeast coast of South Africa. Ichthyol Bull Smith Inst Ichthyol 71: 1-19.

Groombridge, B. (ed.). 1994. 1994 IUCN Red List of Threatened Animals. IUCN, Gland, Switzerland and Cambridge, UK.

IUCN. 1990. IUCN Red List of Threatened Animals. IUCN, Gland, Switzerland and Cambridge, UK.

IUCN. 2010. IUCN Red List of Threatened Species (ver. 2010.2). Available at: http://www.iucnredlist.org. (Accessed: 29 June 2010).

IUCN Conservation Monitoring Centre. 1988. 1988 IUCN Red List of Threatened Animals. IUCN, Gland, Switzerland and Cambridge, UK.

James, N.C., Whitfield, A.K. and Cowley, P.D. 2008. Long-term stability of the fish assemblages in a warm-temperate South African estuary. Estuarine, Coastal and Shelf Science 76: 723-738.

Vorwerk, P.D., Froneman, P.W., Paterson, A.W. and Whitfield A.K. 2008. Fish community response to increased river flow in the Kariega Estuary, a freshwater-deprived, permanently open souther African system. African Journal of Aquatic Science 33: 189-200.

Vorwerk, P.D., Froneman, P.W., Paterson, A.W., Strydom, N.A. and Whitfield, A.K. 2008. Biological responses to a resumption in river flow in a freshwater-deprived, permanently open Southern African estuary. Water SA 34: 597-604.

Whitfield, A.K. 1995. Threatened fishes of the world: Syngnathus watermeyeri Smith, 1983 (Syngnathidae). Environmental Biology of Fishes 43: 152.

Whitfield, A.K. and Bruton, M.N. 1996. Extinction of the river pipefish Syngnathus watermeyeri in the Eastern Cape Province, SouthAfrica. South African Journal of Zoology 92: 59-61.


Citation: Sorensen, M. & Bills, R. 1996. Syngnathus watermeyeri. The IUCN Red List of Threatened Species. Version 2014.2. <www.iucnredlist.org>. Downloaded on 02 September 2014.
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