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SGS Product & Process Certification - Marine Stewardship Council

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Figure 3.Indices of the abundance of juvenile bass year-classes in the Thames Estuary (IVc),<br />

1994-2008 (source CEFAS).<br />

Fishery-independent estimates of relative abundance of juvenile bass year classes are also<br />

available from a trawl survey (actually using a 3-m beam trawl to sample pre-recruit flatfish)<br />

conducted in the Westscheldt Estuary (IVc) by IMARES each year, Figure 4 (source Henk<br />

Heessen, WGNEW). These also show an increasing trend in year class strength since the<br />

early 1990s, though the pattern is not the same as that in the Thames Estuary survey, probably<br />

because different age groups are used in calculating the indices (0-groups especially can suffer<br />

high mortality in cold winters).<br />

N per hour<br />

120<br />

100<br />

80<br />

60<br />

40<br />

20<br />

Figure 4. Indices of the abundance of juvenile bass year classes in the Westscheldt Estuary<br />

from the IMARES DFS (source Henk Heessen, WGNEW).<br />

3.2 Stock status<br />

Sea bass Westerscheldt<br />

0<br />

1970 1975 1980 1985 1990 1995 2000 2005 2010<br />

The results of the fleet-based separable model for the sea bass stock unit (Divisions IVb,c) that<br />

includes the southern North Sea indicate levels of F around 0.2–0.4 between 1995 and 2004<br />

(Pawson et al., 2007b). The gear selectivity patterns derived from the model confirm the results<br />

of Pawson et al. (2005).The abundance of adult bass (SSB) in the North Sea appears to have<br />

remained stable between 1985 and 2004, whilst there has been an increased level of recruitment<br />

from 1989 onwards.<br />

The patterns in F and recruitment derived from this model are consistent with the evidence<br />

provided by the CEFAS logbook scheme and the fishery-independent pre-recruit survey (which<br />

has not been used in the model), but there are inevitable problems with the scaling of F and<br />

estimating biomass. In particular, the absence of data for the recreational rod-and-line fishery,<br />

a substantial contributor to mortality on the younger sea bass, would affect estimates of<br />

recruitment to the commercial fishery. However, these are consistent between areas over the<br />

period 1984–2002, and that for VIId closely matches the fishery-independent abundance<br />

indices for pre-recruit bass provided by the Solent trawl survey that covers the main nursery<br />

areas for sea bass in Division VIId. Thus, whilst the model reflects reasonably the dynamics of<br />

the bass stock (around the UK) both in stock numbers, SSB and in F, it is not possible to<br />

Page 22 of 151

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