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Tanga Fisheries Analysis - IUCN

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Figure 21 - Proportion of Monthly Catch of Lethrinidae (Ngalawa/Mishipi)<br />

Proportion of Monthly Catch<br />

Lethrinidae Caught by Ngalawa/Mishipi<br />

1<br />

0.9<br />

0.8<br />

0.7<br />

0.6<br />

0.5<br />

0.4<br />

0.3<br />

0.2<br />

0.1<br />

0<br />

1995 10<br />

1996 1<br />

1996 4<br />

1996 7<br />

1996 10<br />

1997 1<br />

1997 4<br />

1997 7<br />

1997 10<br />

1998 1<br />

1998 4<br />

1998 7<br />

1998 10<br />

1999 1<br />

1999 4<br />

1999 7<br />

1999 10<br />

2000 1<br />

2000 4<br />

2000 7<br />

2000 10<br />

2001 1<br />

2001 4<br />

2001 7<br />

2001 10<br />

2002 1<br />

2002 4<br />

2002 7<br />

2002 10<br />

2003 1<br />

2003 4<br />

2003 7<br />

2003 10<br />

Proportion of Total Monthly Catch<br />

2004 1<br />

2004 4<br />

2004 7<br />

Year/Month<br />

Figure 22 presents data on catches of Lethrinidae using madema. The data show a very strong<br />

seasonality in the capture these species, with clear peaks at the same time of year (Kusi) as with<br />

the mishipi fishery, but with very few data outside of this period. In both cases, the same type of<br />

vessel is being used, but Lethrinidae appear to be much more seasonally available. The question<br />

of whether the fishers are operating in different grounds might be accounted for by the fact that the<br />

peaks in Lethrinidae are at approximately the same time each year. So assuming the fishers are<br />

using the same grounds each year, these data would seem to indicate a strong seasonal variation<br />

in Lethrinidae’s vulnerability to madema. Again there is little in the way of an apparent increase in<br />

the relative abundance of these species in the catch.<br />

Figure 22 - Proportion of Monthly Catch of Lethrinidae (Ngalawa/Madema)<br />

Proportion of Monthly Catch<br />

Lethrinidae Caught by Ngalawa/Madema<br />

Proportion of Total Monthly Catch<br />

1<br />

0.9<br />

0.8<br />

0.7<br />

0.6<br />

0.5<br />

0.4<br />

0.3<br />

0.2<br />

0.1<br />

0<br />

1995 10<br />

1996 1<br />

1996 4<br />

1996 7<br />

1996 10<br />

1997 1<br />

1997 4<br />

1997 7<br />

1997 10<br />

1998 1<br />

1998 4<br />

1998 7<br />

1998 10<br />

1999 1<br />

1999 4<br />

1999 7<br />

1999 10<br />

2000 1<br />

2000 4<br />

2000 7<br />

2000 10<br />

2001 1<br />

2001 4<br />

2001 7<br />

2001 10<br />

2002 1<br />

2002 4<br />

2002 7<br />

2002 10<br />

2003 1<br />

2003 4<br />

2003 7<br />

2003 10<br />

2004 1<br />

2004 4<br />

2004 7<br />

Year/Month<br />

So overall, there is little evidence that the populations of the groups that these species belong to<br />

are showing any sort of dramatic recovery in abundance. This might be because the period since<br />

the beach-seine ban was introduced is still relatively short and it might also be because the ban on<br />

both beach-seining and dynamite-fishing is not complied with. There is evidence for example from<br />

TCZCDP records that the use of beach-seines persists (TCZCDP Mid-Term Review, 2001).<br />

33

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