State of the Bay Report 2011-Final.pdf - Anchor Environmental
State of the Bay Report 2011-Final.pdf - Anchor Environmental
State of the Bay Report 2011-Final.pdf - Anchor Environmental
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
<strong>State</strong> <strong>of</strong> Saldanha <strong>Bay</strong> & Langebaan Lagoon <strong>2011</strong><br />
Sediments<br />
iron are commonly used as normalizes for trace metal content as <strong>the</strong>y ubiquitously coat all<br />
sediments and occur in proportion to <strong>the</strong> surface area <strong>of</strong> <strong>the</strong> sediment (Gibbs 1994); <strong>the</strong>y are<br />
abundant in <strong>the</strong> earth’s crust and are not likely to have a significant anthropogenic source (Gibbs<br />
1994, Summers et al. 1996); and ratios <strong>of</strong> metal concentrations to Al or Fe concentrations are<br />
relatively constant in <strong>the</strong> earth’s crust (Summers et al. 1996). Normalized metal/aluminium ratios<br />
can be used to estimate <strong>the</strong> extent <strong>of</strong> metal contamination within <strong>the</strong> marine environment, and to<br />
assess whe<strong>the</strong>r <strong>the</strong>re has been enrichment <strong>of</strong> metals from anthropogenic activities. In this study<br />
metal concentrations were normalized against (divided by) aluminium and not iron due to <strong>the</strong><br />
known anthropogenic input <strong>of</strong> iron from <strong>the</strong> iron ore quay and industrial activity in Saldanha <strong>Bay</strong>.<br />
Figure 5.19. Metal:Al ratios for Copper, Lead, Cadmium and Nickel for sediments sampled in <strong>2011</strong> from<br />
Saldanha <strong>Bay</strong>-Small <strong>Bay</strong> (SB), Big <strong>Bay</strong> (BB), Langebaan Lagoon (LL), Donkergat (D) and<br />
Salamander <strong>Bay</strong> (S)<br />
Metal enrichment factors were calculated for Cd, Pb and Cu relative to <strong>the</strong> 1980 sediments<br />
(Table 5.4). Unfortunately historic enrichment factors could not be calculated for Ni as no data was<br />
available for this metal in 1980. Enrichment factors equal to (or less than) 1 indicate no elevation<br />
relative to pre-development sediments, while enrichment factors greater that 1 indicate a degree <strong>of</strong><br />
metal enrichment within <strong>the</strong> sediments over time. Enrichment factors were not calculated for<br />
Langebaan Lagoon since all concentrations were below <strong>the</strong> detection limits.<br />
5.4.2.1 Cadmium<br />
Cadmium (Cd) is a trace metal used in electroplating, in pigment for paints, in dyes and in<br />
photographical process. The likely sources <strong>of</strong> Cd to <strong>the</strong> marine environment are in emissions from<br />
industrial combustion process, from metallurgical industries, from road transport and waste streams<br />
(OSPAR 2010). A likely point source for Cd contamination in <strong>the</strong> marine environment is that <strong>of</strong><br />
stormwater drains. Cd is toxic and liable to bioaccumulation, and is thus a concern for both <strong>the</strong><br />
marine environment and human consumption (OSPAR 2010). The Cd concentrations detected in<br />
<strong>2011</strong> exceeded <strong>the</strong> ERL prescribed by NOAA at <strong>the</strong> Yacht Club Basin and at <strong>the</strong> multi-purpose quay<br />
(Figure 5.20 and Table 5.3). Both areas had a relatively high mud content which suggests that <strong>the</strong>se<br />
areas are subject to high retention rates. The normalized Cd:Al ratios were high at <strong>the</strong> Yacht Club<br />
107<br />
ANCHOR<br />
e n v i r o n m en t a l