Red List of South African Species

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Vulnerable (VU)

Rationale

Rhabdosargus globiceps (White Sumptnose) is distributed in southern Africa from southern Angola to South Africa. It occurs in rocky reefs up to 120 m depth. This species is an important component of commercial and recreational linefisheries in South Africa where four separate stocks have been reported between Port Nolloth and the Kei River: Western Cape, Southwestern Cape, Southern Cape and Southeastern Cape. White Stumpnose is also caught as bycatch by inshore trawlers on the Southeastern and Southern Cape coasts. Catches and CPUE of R. globiceps in South Africa have decreased substantially in all areas of its distribution, particularly in the Southern Cape. In the south-western Cape, standardized CPUE shows a greater than 50% decline in the last decade. There is limited information on population trends and catch data from Angola and Namibia, however, in over half of this this species' range (Total EOO = 372,663.52 km2; South African EOO = 206,749.14 km2) there have been significant recorded declines (over 70% over the last 100 years). This species is afforded some protection in marine protected areas throughout its range and a minimum landing size of 25 cm is implemented in South Africa. Rhabdosargus globiceps is a long-lived species up to 21 years with a generation length of nine years, life history characteristics that are attributed to elevated risk of extinction. Given the significant population declines recorded from South Africa, we infer population declines over its entire range to exceed the thresholds (30%) over three generations for listing of Vulnerable under A2. This species is listed as Vulnerable under A2bd. We strongly recommend examination of the status of its population throughout its range. 


Distribution

Rhabdosargus globiceps is endemic to southern Africa and is known from southern Angola to the Kei River on the east coast of South Africa (Whitfield 1998). This species is also known from Luderitz in Namibia (B. Mann pers. obs.). The depth range for this species is from shore to 120 m (Heemstra and Heemstra 2004). The extent of occurrence (EOO) for this species' entire range is 372,663.52 km2 and the EOO for its South African range is 206,749.14 km2.

Population trend

Trend

Rhabdosargus globiceps is an important recreational and commercial linefish off the west and south coasts of South Africa (Bennett 1991, Sauer et al. 1997) and is also taken as a bycatch by inshore trawlers (Japp et al.1994) and beach-seine fishers (Lamberth et al. 1994, 1995). In South Africa, the stock of Rhabdosargus globiceps is considered to have collapsed with spawning biomass per recruit below 25% but the results of the analysis were speculative without a reliable measure of natural mortality (Arendse 2011). However, there is additional evidence that suggests that the stocks on the Southern Cape coast and on the west of Cape Peninsula, and Table Bay have collapsed (Attwood and Kerwath 2012). There are four separate stocks of R. globiceps between Port Nolloth and the Kei River: Western Cape (Saldanah Bay), Southwestern Cape, Southern Cape and Southeastern Cape (Griffiths et al. 2002). A comprehensive stock assessment has not been conducted on R. globiceps; however, catch rates of commercial linefishers declined over the past 100 years by as much as 68% off the West Coast, 52% off the Southwestern Cape and 99.8% off the Southern Cape (Griffiths 2000). The severe decline in the Southern Cape is probably because the stock is also trawled in this area (Griffiths et al. 2002). Recorded commercial catches have declined considerably since the late 1980s (NMLS unpublished data). Catch data from Angola and Namibia are limited for this species.

Commercial data show that since 2000 commercial fishing effort has declined dramatically in the South African line fishery from approximately 3,000 to 450 vessels in line with the long-term rights allocation in 2006 (Department of Agriculture, Forestry and Fisheries 2012). 



Threats

Based on the slow growth rate and maximum age of more than 20 years, R. globiceps is vulnerable to overfishing (Griffiths et al. 2002). In parts of its distribution R. globiceps is also threatened by nursery habitat destruction (e.g. by harbour development in Saldanah Bay) and pollution.

Uses and trade

Rhabdosargus globiceps is an important recreational and commercial linefish off the west and south coasts of South Africa (Bennett 1991, Sauer et al. 1997) and is also taken as a bycatch by inshore trawlers (Japp et al. 1994) and beach-seine fishers (Lamberth et al. 1994, 1995). Estimated annual landings during the 1990s were ~ 40 tonnes for shore anglers, 147 tonnes for commercial linefishers, 12.5 tonnes for beach-seine operators and 14-30 tonnes for inshore trawlers (Griffiths et al. 2002). Recreational and commercial linefisherman catch this species on the south coast and in False Bay, but much larger quantities are caught on the west coast in Saldanha Bay (approximately 80 tonnes per annum). This species used to be netted by beach seines in large quantities in Hout Bay, Blouberg and Melkbos, but these stocks have collapsed entirely (Attwood and Kerwath 2012), which raises concern about the vulnerability of the species. Estuarine anglers catch juvenile fish in estuaries from the Berg River in the west to the Kowie River in the east (Whitfield 1998). This species is occasionally caught as bycatch of gillnet fisheries on the West Coast (Hutchings and Lamberth 2002).

Conservation

Current regulations for Rhabdosargus globiceps include a minimum size limit of 25 cm TL and a daily bag limit of ten fish per person per day, applying only to recreational and subsistence fishers (Department of Agriculture, Forestry and Fisheries 2012). In addition to fisheries legislation, R. globiceps receives some protection in the Langebaan Lagoon which is part of the West Coast National Park (Attwood et al. 2007, Kerwath et al. 2008) and is likely to receive some protection in no-take MPAs on the eastern seaboard including De Hoop and Tsitsikamma (C. Buxton and B. Mann pers. comm. 2009). Similarly the no-take areas within the Table Mountain National Park MPA should provide some protection. L. de Vos (UCT, unpublished data) recorded this species in the Stilbaai MPA during a BRUV survey and trawl records indicated the presence of this species in the vicinity of the Bird Island MPA (Wallace et al. 1984).

It is recommended that the bag limit for recreational anglers should be reduced to five per person per day, as this species is moderately long-lived and easily caught. Attention should also be given to the protection of the respective nursery grounds, particularly at Saldanha where industrial threats to the beaches are of concern. The species is poorly represented in offshore MPAs, particularly on the Agulhas Bank (Attwood and Kerwath 2012). 


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