BEN SCHOEMAN DOCK BERTH DEEPENING Specialist ... - Transnet
BEN SCHOEMAN DOCK BERTH DEEPENING Specialist ... - Transnet
BEN SCHOEMAN DOCK BERTH DEEPENING Specialist ... - Transnet
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Figure 21a: Predicted number of days during which copper concentrations (a sensitive<br />
proxy for all trace metals) in the surface layer do not comply with RSA water quality<br />
guidelines for the maintenance of ecosystems. (Winter, Cutter Suction Dredger; copied<br />
from Figure B.7.12, Van Ballegooyen et al., 2006)<br />
Particulate trace metal concentrations above the threshold effect level (TEL) may exert<br />
toxic effects on the biota of the harbour in the water column, on the hard structures or in<br />
the sediments. Tables 9 and 11 show that a large proportion of the sediments exceed<br />
the TEL level for more than one of the trace metals. Consequently over and above the<br />
possible effects of inundation the dredging may redistribute sediments that may be toxic<br />
at the TEL level and above. Direct toxicity effects of contaminated sediments on bivalve<br />
embryos have been measured by Geffard et al. (2002). The sediments tested covered a<br />
wide range from heavily contaminated (24.6mg/kg PAH, 136.8mg/kg copper, 568mg/kg<br />
zinc) to lower contamination levels at 2mg/kg PAH, 7.6mg/kg copper and 73mg/kg zinc.<br />
Note that the defined toxicity effect was chronic deformations in 20% of oyster embryos<br />
after 24 hour exposures (=24hr EC 20 ); this can be considered to be a low toxicity effect<br />
level. For sediments comparable to those in the Ben Schoeman Dock Basin Geffard et<br />
al.'s (2002) data indicate that such toxicity effects may be generated at 2000mg/l<br />
suspended sediment. This is a high concentration and is not predicted to occur<br />
anywhere outside of the immediate dredge area (Figure 20).<br />
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