Red List of South African Species

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Least Concern (LC)

Rationale

The zebra (Diplodus hottentotus) occurs from False Bay to southern Mozambique to depths of 120 m. There is an isolated subpopulation in Angola. Currently, no major threats or population declines have been identified for this species. However, D. hottentotus is a slow growing, and late maturing species that exhibits high residency which make it susceptible to possible overexploitation. This species is targeted by subsistence and recreational fishers but has been decommercialized (no sale). Diplodus hottentotus is also afforded some protection by the no-take MPAs along the South African coast. It is listed at Least Concern.

Distribution

Diplodus hottentotus is an endemic species occurring from False Bay, South Africa, to southern Mozambique and has a depth range from zero to 120 m (Pereira 2000, Heemstra and Heemstra 2004). There is an isolated subpopulation found in southern Angola (Winkler 2013).

Population trend

Trend

Although no formal stock assessments have been undertaken on Diplodus hottentotus, angler surveys conducted along the KwaZulu-Natal coast showed little change in CPUE between 1975–1977 (0.005 fish/angler/day), 1994-1996 (0.004 ffish/angler/day) and 2009–2010 (0.006 fish/angler/day) (Joubert 1981, Mann et al. 1997, Dunlop and Mann 2012). An increase in CPUE was recorded between 1985–1986 (3.03 g/person/hour) to 1994-1996 (6.0 g/person/hour) in the Eastern Cape (Clarke and Buxton 1989, Brouwer 1997). Long-term monitoring of shore angler catches from 1985 to 2008 in KwaZulu-Natal from the National Marine Linefish System (NMLS) also showed little change in CPUE (National Marine Linefish System unpublished data). Percent catch composition fluctuated from 0.04% in 1975-1977, 0.038% in 1994-1996 to 0.52% in 2009-2010 in KwaZulu-Natal (Joubert 1981, Mann et al. 1997, Dunlop and Mann 2012). A decrease was recorded from 1985–1986 (2.0%) to 1994–1996 (0.7%) in the Eastern Cape (Clarke and Buxton 1989, Brouwer 1997).

Threats

Currently, no major threats to D. hottentotus have been identified; however, this species exhibits slow growth, late maturation, longevity, and high residency, which make it more vulnerable to overexploitation (Mann and Dunlop 2012). Ongoing catch and effort monitoring and completion of a stock assessment are recommended.

Uses and trade

Diplodus hottentotus is primarily caught in the shore fishery and is of moderate importance throughout its distribution (Joubert 1981, Whibley and Garratt 1989, van der Elst 1993, Brouwer 1997, Brouwer et al. 1997, Mann et al. 2003, Dunlop and Mann 2012). Larger specimens are occasionally shot by spearfishers or caught by skiboat fishers (Mann et al. 1997, Mann and Attwood 2000, Dunlop and Mann 2013). This species is a no-sale recreational only species and may not be caught and sold in commercial fisheries (Department of Agriculture, Forestry and Fisheries 2012).

Conservation

Current regulations for D. hottentotus include a daily bag limit of five fish per person per day for recreational and subsistence fishers, a minimum landing size of 30 cm TL, and it has been decommercialized (no sale) (Department of Agriculture, Forestry and Fisheries 2012). This species is also afforded some protection in a number of no-take MPAs in southern Africa, inter alia De Hoop (Bennett and Attwood 1991, 1993), Still Bay, Tsitsikamma (Cowley et al. 2002), Bird Island, Dwesa-Cwebe (Venter and Mann 2012) Pondoland (Mann et al. 2006), Aliwal Shoal, St Lucia and Maputaland MPAs (World Database of Protected Areas, accessed March 2014).

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