Population trend
Trend
There is a high degree of fragmentation within the Rhabdosargus sarba complex with limited information on population or stock status throughout its distribution. In South Africa, Rhabdosargus sarba was assessed in KwaZulu-Natal and it was found that the adult stock was not overexploited (SB/R = 63%, F=0) before 2002; however, data from a per-recruit analysis conducted for the KwaZulu-Natal coast indicate that the stock is overexploited and has been reduced to 25–40% of its spawning biomass per recruit while the juvenile stock in estuaries is experiencing high fishing mortality (SB/R = 34%, F=0) (James et al. 2004). More recent research has shown a decline in the CPUE of the adult population with the closure of the St Lucia estuarine system due to prevailing drought conditions (Mann and Pradervand 2007), which forms an important nursery area for this species (Wallace 1975a). No major changes in CPUE of the adult population have been observed between 2004 and 2012 (Mann 2012). An increase in mean size was recorded in St Lucia MPA between 2001 and 2005 and is attributed to a lack of recruitment into the adult population because of the closure of the St. Lucia mouth (Mann and Pradervand 2007, Mann 2012). There was a substantial decline in percentage composition of shore anglers catches along the KwaZulu-Natal coast between 1994–1996 (2.28%) and 2009–2010 (0.24%) (Mann et al. 1997, Dunlop 2011). Decline recorded in the St Lucia MPA between 2001–2005, attributed to closure of St Lucia mouth (Mann 2012).
Persian Gulf
Grandcourt et al. (2011) compiled size frequency data for Rhabdosargus sarba in the southern Persian Gulf from commercial catches made off the coast of the Emirate of Abu Dhabi in the United Arab Emirates between September 2008 and August 2009. Biological data were collected from individuals purchased from commercial catches during the same time period. The mean age and size at sexual maturity for male Rhabdosargus sarba was 2.0 years and 23.5 cm Lm and 2.1 years and 23.7 cm Lm for females. The ratio of males to females in the southern Persian Gulf was estimated as 1:1.4 (M:F), though Grandcourt et al. (2011) noted the samples were significantly female biased. Grandcourt et al. (2011) estimated the natural, fishing and total mortality for Rhabdosargus sarba to be 0.27 year-1, 0.77 year-1, and 1.04 year-1, respectively. The mean age and size at first capture was 0.59 years and 14.0 cm Lc50. Juvenile retention for Rhabdosargus sarba was 74.0%. Grandcourt et al. (2011) concluded that Rhabdosargus sarba is overexploited in the Persian Gulf due to its estimated fishing mortality (0.77 year-1), which was considerably greater than F0.1 (0.39). The fishing mortality was also greater than both biological reference points, target (FSB40 = 0.22) and limit (FSB30 = 0.30). Relative spawner biomass per recruit was estimated to be 6.4% of the theoretical unexploited level at the fishing mortality rate 0.77 year-1, indicating both growth and recruitment overfishing were occurring.
Annual Fisheries Statistics Report for Abu Dhabi Emirate (2005-2012)
Abu Dhabi Emirate fisheries collected, on average, 52.89 tonnes of Rhabdosargus sarba between 2005–2012. A peak of 127.5 tonnes were collected in 2007, followed by a decline to 17.7 tonnes in 2011. There was a slight increase to 24.7 tonnes in 2012.
Catches from Bahrain decreased overall from 2009–243.2 tonnes , 2010–171.9 tonnes, to 119.3 tonnes in 2011. This species is not reported from Kuwait (Bishop pers comm. 2013), or Qatar.
FAO production statistics from Taiwan mostly come from mariculture. Rhabdosargus sarba is rarely caught in the wild (W. Liao pers. comm. 2009). FAO production figures in 2007 were: Australia (Eastern Indian Ocean) - 2,563 tonnes, (Southwest Pacific) - 215 tonnes, (Western Central Pacific) - 521 tonnes, Japan - 15,600 tonnes, Republic of Korea - 686 tonnes, Taiwan - 1,648 tonnes and New Zealand (Southwest Pacific) 5,919 tonnes. In New South Wales, Australia, between 1995–1996 and 2005–2006, landings averaged ~53 tonnes per year worth an estimated AU$240,000 a year (NSW DPI Catch Statistics).