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State of the Bay Report 2011-Final.pdf - Anchor Environmental

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<strong>State</strong> <strong>of</strong> Saldanha <strong>Bay</strong> & Langebaan Lagoon <strong>2011</strong><br />

Sediments<br />

5.4.3 Summary<br />

A multivariate analysis was conducted using PRIMER to determine <strong>the</strong> similarity (Euclidean distance)<br />

between sites based on <strong>the</strong> concentrations <strong>of</strong> <strong>the</strong> different trace metals in <strong>the</strong> sediments. The<br />

results are presented graphically in Figure 5.29 with different colour symbols indicating significant<br />

groupings <strong>of</strong> sites. These are organized based on <strong>the</strong> general relative concentrations <strong>of</strong> trace metals,<br />

with <strong>the</strong> red (A) indicating <strong>the</strong> highest concentrations and <strong>the</strong> blue (E) <strong>the</strong> lowest. The highest<br />

concentrations <strong>of</strong> all <strong>the</strong> trace metals measured were recorded at <strong>the</strong> Yacht Club Basin, <strong>the</strong> only<br />

exception being lead which was greater at <strong>the</strong> multi-purpose quay. This result correlates well with<br />

that <strong>of</strong> <strong>the</strong> particle size composition results which indicated that <strong>the</strong> Yacht Club Basin harboured <strong>the</strong><br />

highest mud fraction. This suggests that a primary factor responsible for <strong>the</strong> high trace metal<br />

concentration is <strong>the</strong> poor flushing <strong>of</strong> fine sediments from this area. This is consistent with results<br />

observed since 2008. The grouping <strong>of</strong> most <strong>of</strong> <strong>the</strong> Small <strong>Bay</strong> sites into <strong>the</strong> category with <strong>the</strong> second<br />

highest concentrations <strong>of</strong> trace metals indicated that Small <strong>Bay</strong> had been subjected to a greater<br />

extent <strong>of</strong> contamination compared to Big <strong>Bay</strong> and Langebaan Lagoon. This is attributable to <strong>the</strong><br />

poor circulation and flushing in Small <strong>Bay</strong> in combination with trace metal contamination by <strong>the</strong><br />

surrounding industries and activities. The groups <strong>of</strong> sites with moderate to low concentrations <strong>of</strong><br />

trace metals were not grouped spatially, but ra<strong>the</strong>r spread throughout Big <strong>Bay</strong> and Langebaan<br />

Lagoon. This indicates that <strong>the</strong> retention <strong>of</strong> trace metals varies spatially, most likely due to<br />

variations in depth and current strengths at different localities. Interestingly, Sites S1 and D1,<br />

positioned in Salamander <strong>Bay</strong> and Donkergat, respectively, grouped with <strong>the</strong> Yacht Club Basin and<br />

multi-purpose quay indicating that <strong>the</strong>y are most similar based on <strong>the</strong> concentrations <strong>of</strong> trace<br />

metals. This indicates that <strong>the</strong>se areas have been subject to high levels <strong>of</strong> trace metal<br />

contamination, most likely attributable to recent dredging activities in this part <strong>of</strong> <strong>the</strong> <strong>Bay</strong>. The low<br />

mud content at Donkergat and Salamander indicates that <strong>the</strong>se areas are well flushed and it is<br />

probable, in <strong>the</strong> absence <strong>of</strong> fur<strong>the</strong>r dredging, that trace metal concentrations will decline again over<br />

time.<br />

Elevated trace metal concentrations recorded in Saldanha <strong>Bay</strong> in 1999 were ascribed to an<br />

accumulation <strong>of</strong> <strong>the</strong>se metals in <strong>the</strong> sediments <strong>of</strong> <strong>the</strong> <strong>Bay</strong> over <strong>the</strong> preceding 20 years, much <strong>of</strong><br />

which was re-suspended as a result <strong>of</strong> dredging operations and had settled in <strong>the</strong> surface layers.<br />

Construction <strong>of</strong> <strong>the</strong> Marcus Island causeway and <strong>the</strong> ore terminal had contributed to this process by<br />

reducing wave action and modifying circulation patterns prevailing in <strong>the</strong> <strong>Bay</strong>. Subsequent<br />

monitoring has revealed a substantial overall decrease in <strong>the</strong> concentrations <strong>of</strong> metals in <strong>the</strong> <strong>Bay</strong>,<br />

suggesting that a disturbance, like dredging which remobilises <strong>the</strong> fine sediments and re-suspends<br />

metals, can severely affect <strong>the</strong> health <strong>of</strong> <strong>the</strong> <strong>Bay</strong> and that it takes between three to six years before<br />

<strong>the</strong> contaminated sediments are removed from <strong>the</strong> <strong>Bay</strong> by natural processes. It was also shown that<br />

metal concentrations were elevated near <strong>the</strong> Multi-purpose Quay as a result <strong>of</strong> lead and copper ore<br />

dust entering <strong>the</strong> environment during export activities. In addition, metal concentrations were high<br />

(<strong>of</strong>ten exceeding ERL values) in <strong>the</strong> Yacht Club Basin and this may be due to <strong>the</strong> fact that this area is<br />

a depositional zone for fine grained sediments and organic matter onto which metals adsorb.<br />

121<br />

ANCHOR<br />

e n v i r o n m en t a l

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