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BEN SCHOEMAN DOCK BERTH DEEPENING Specialist ... - Transnet

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6.2.3.2 Alteration of benthic biological communities through toxins associated with<br />

dredge spoil<br />

The dredge spoil is characterised by trace metal concentrations within the LC special<br />

care (action level) range and higher than threshold effect levels (TEL). It therefore has<br />

the potential to alter benthos community structure on the site used for spoil dumping and<br />

immediately adjacent areas. Because of differing benthos community structure in the two<br />

candidate sites identified for spoil discharge there are varying implications of this.<br />

Therefore, as for the effects of inundation by dredge spoil, the two sites are assessed<br />

separately.<br />

SITE #1:<br />

Nature of impact – Trace metal contaminated dredge spoil exerts toxic effects on<br />

benthos in the dredge spoil dump area and the immediately adjacent seabed and alters<br />

benthic communities.<br />

Extent – Local; restricted to the immediate area of the spoil dump area<br />

Duration – Short: The toxicity potential of the dumped sediments depends on the<br />

bioavailability of trace metals which should be limited due to probable adsorption to iron<br />

(ferric) and manganese (manganous) hydroxides present in the now oxic sediments.<br />

Trace metals should thus remain in the particulate phase. This is borne out by simulation<br />

modelling results showing that RSA water quality guideline concentrations for copper are<br />

not transgressed at any stage for any of the spoil dumping scenarios at either of the<br />

spoil dump sites (Van Ballegooyen et al., 2006).<br />

Tests with sediments comparable to those targeted for dumping indicate generally low<br />

toxicity effects (Geffard et al. 2002). Further, if the sediment is sufficiently toxic to cause<br />

deleterious effects the toxicity should be relatively rapidly dissipated by wave generated<br />

resuspension and advection of silt and clay sized particles away from the dump site<br />

area. Re-deposition of these sediments away from the dump site should be sufficiently<br />

small to mitigate any latent toxicity (above). Therefore any toxic effects on biota in and<br />

adjacent to the dump site should be worked out of the community within a few<br />

generations.<br />

Intensity –Low; toxicity effects should be minimal due to retention of trace metals in the<br />

inorganic particulate phase.<br />

Probability – Improbable; there is only one instance of a trace metal exceeding the PEL<br />

level and this should be reduced below this threshold through dilution with less<br />

contaminated sediments in the dredging and spoil dumping process<br />

Status of impact – Negative<br />

Degree of confidence – High<br />

Significance – Insignificant; the spatial and temporal extent of any effect should be<br />

small relative to the amount of similar habitat in Table Bay.<br />

Mitigation – None<br />

Impact Assessment Table<br />

No<br />

Mitigation<br />

Extent Intensity Duration Consequence Probability Significance Status Confidence<br />

Local Low Shortterm<br />

Very Low Improbable INSIGNIFICANT -ve High<br />

1 1<br />

3<br />

1<br />

Mitigation n/a n/a n/a n/a n/a n/a n/a n/a<br />

78

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