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BEN SCHOEMAN DOCK BERTH DEEPENING Specialist ... - Transnet

BEN SCHOEMAN DOCK BERTH DEEPENING Specialist ... - Transnet

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harbour. No benthos sampling results have been reported for the Ben Schoeman Dock<br />

Basin or the outer areas of the harbour that would allow a determination of the extent of<br />

the apparent pollution effect on benthos distributions. AVS values do tend to decline in<br />

these areas and may be zero indicating that the sediments are oxic. If, as is likely,<br />

anoxia is the controlling variable it is probable that there will be benthos in the sediments<br />

with low to zero AVS levels. Distortion levels in community composition due to pollution<br />

effects or other stressors such as frequent surficial sediment suspension are, however,<br />

unknown.<br />

Outside the harbour, large numbers of juvenile rock lobsters can be found on the vertical<br />

faces of the outer harbour wall (Hazell et al. 2002). Other major components of the wall<br />

community are encrusting corallines, the barnacle Notomegabalanus algicola, the sea<br />

urchin Parechinus angulosus, the ribbed mussel Aulacomya ater, and sponges (Mayfield<br />

1998). The relatively low coverage and biomass of mussels and the high cover of<br />

encrusting corallines at the wall contrast with nearby natural subtidal rocky shores, for<br />

example at Mouille Point, where mussels cover approx. 80% of the rocks and encrusting<br />

coralline cover is low (Mayfield 1998, Table 1).<br />

Harbours are a typical location for the introduction of alien species through ships calling<br />

at the port which may transport organisms on their hulls or in their ballast waters.<br />

Examples in the Port of Cape Town are the European shore crab Carcinus maenas, the<br />

anemone Metridium senile, which grows on loose, silt-laden boulders or other objects,<br />

and on the soft sediments on the floor of the Victoria and Alfred Basins, the red algae<br />

Schimmelmannia elegans, and the ascidian Ciona intestinalis (Robinson et al. 2005).<br />

Table 1: Average percentage cover and wet biomass (± standard error) of benthic<br />

organisms at the outer harbour wall and at Mouille Point. Percentage cover includes<br />

secondary cover (e.g. barnacle cover) and can thus exceed 100% (after Mayfield 1998).<br />

Benthos<br />

Harbour Wall<br />

%cover / g wet mass/m 2 ± SE<br />

Mouille Point<br />

%cover / g wet mass/m 2 ± SE<br />

Coralline algae 75 / 2235 ± 289 20 / 506 ± 192<br />

Foliar algae

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