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icolls - Sustainable Tourism CRC

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ECOLOGY, THREATS AND MANAGEMENT OPTIONS FOR SMALL ESTUARIES AND ICOLLS<br />

Table 10: Dietary categories in the stomach contents of S. ciliata and M. cephalus in Belongil and Tallows<br />

Creeks<br />

Species Sillago ciliata Mugil cephalus<br />

ICOLL Belongil Creek Tallows Creek Belongil Creek Tallows Creek<br />

Number n=27 n=2 n=10 n=13<br />

Taxa %F %N %V %F %N %V %F %N %V %F %N %V<br />

Crustacea - - - 50.0 8.2 7.5 - - - 7.7 98.1 4.6<br />

Decapoda - - - 50.0 0.6 5 - - - - - -<br />

Isopoda - - - - - - - - - - - -<br />

Amphipoda - - - 50 7.6 2.5 - - - 7.7 98.1 4.6<br />

Polychaeta 100.0 41.7 84.3 100.0 2.5 55.0 - - - - - -<br />

Mollusca 44.4 59.7 13.5 50.0 5.0 10.0 - - - - - -<br />

Bivalvia 44.4 59.7 13.5 50.0 5.0 10.0 - - - - - -<br />

Gastropoda - - - - - - - - - - - -<br />

Teleosts - - - - - - - - - - - -<br />

FW Inverts * - - - 100.0 8.4 7.5 - - - 7.7 1.8 0.4<br />

Sediment - - - - - - 50.0 *** 45.0 - - -<br />

Algae 3.7 *** 1.8 - - - 40.0 *** 40.0 92.3 *** 57.3<br />

Plant Material - - - 50.0 *** 2.5 - - - 30.7 *** 2.3<br />

Other 3.7 *** 0.4 50.0 *** 17.5 20.0 *** 15.0 61.5 *** 35.4<br />

%F = Frequency of occurrence, %N = percentage contribution by number, %V = volume of the dietary categories in the stomach contents; *<br />

FW Inverts were collapsed into one category due to the occurrence of specific taxa (Chironomids – S. ciliata, Coleopterans – A. australis and<br />

Hemipterans – M. cephalus); *** indiscrete dietary items inappropriate for numerical classification.<br />

The diet of P. fuscus from Tallows Creek was consistently less diverse than those of the other three teleosts<br />

(Table 9 and 10). Guts from P. fuscus were comprised predominately of decapods of the genus Metapenaeus<br />

(62.5%V), and unidentifiable teleosts (31.67%V) (Table 9 and 10). In Belongil Creek, individuals with gut<br />

contents had only fed on teleosts (Table 9 and 10). Interestingly the diet of P. fuscus generally consisted of a<br />

single large prey item swallowed whole (G. Russell, personal observation).<br />

Reconstructing the diets of M. cephalus individuals is notoriously difficult given their benthic feeding habits<br />

and their tendency to consume large quantities of unidentifiable material. In this study, all individuals had<br />

relatively full stomachs (Table 8). Large quantities of sediment, algae and unidentifiable particulate matter made<br />

up the bulk of diets, except for one large individual collected from Tallows Creek which had consumed<br />

crustaceans and aquatic insects (Table 9 and 10). For that individual, about 10% of the stomach volume was<br />

taken up by these aquatic macroinvertebrates.<br />

Polychaete worms were by far the most commonly consumed prey item in the diet of S. ciliata, as<br />

emphasised by the fact that they were present in all guts (with contents) across both ICOLLs (Table 8).<br />

Volumetrically, polychaetes contributed 84.26% and 55% of the diets of S. ciliata in Belongil and Tallows<br />

Creeks respectively (Table 8). Bivalve molluscs were the second most important item by volume in each location<br />

and were the dominant item ingested by number at Belongil Creek (59.72%). Crustaceans, namely decapods and<br />

amphipods, occurred in 50% of the individuals from Tallows Creek, but none were recorded from the guts of any<br />

of the 27 individuals analysed from Belongil Creek.<br />

Stable isotope analyses<br />

Given the appreciable number of individuals collected with no gut contents (Table 8), there were many more<br />

individuals whose diets were assessed using stable isotope data relative to gut contents data. For example, while<br />

only 27 S. ciliata individuals had prey items in their guts, 36 individuals were available for stable isotope<br />

analyses. This is because stable isotope analyses of diets tend to be based on muscle tissue isotope signatures and<br />

does not therefore rely on the presence of prey items in individual guts.<br />

In many instances, small catch sizes in one or both ICOLLs prohibited comparisons of gut contents and<br />

stable isotope analyses. For example, A. australis and S. ciliata catches in Tallows Creek were extremely low<br />

(relative to Belongil Creek) so comparisons of the two methods were only possible for the Belongil Creek<br />

individuals. Similarly, there were too few individuals (with and without gut contents) to facilitate comparisons<br />

between gut contents and stable isotope dietary reconstructions for P. fuscus (Table 8).<br />

41

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