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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 />

Water quality<br />

The mussel samples are analysed for <strong>the</strong> metals cadmium (Cd), copper (Cu), lead (Pb), zinc<br />

(Zn), iron (Fe) and manganese (Mn), hydrocarbons and pesticides. A new automated method for<br />

sample preparation, including microwave digestion, has recently been adopted (Watling 1981; G.<br />

Kiviet pers. comm.). Data from <strong>the</strong> mussel watch programme are represented in Figure 4.9 where<br />

<strong>the</strong> maximum legal limits prescribed for each contaminant in shellfish for human consumption in<br />

South Africa, as stipulated by <strong>the</strong> Regulation R.500 (2004) published under <strong>the</strong> Foodstuffs, Cosmetics<br />

and Disinfectants Act, 1972 (Act 54 <strong>of</strong> 1972), are indicated in red text. Where guidelines have not<br />

been specified in national legislation those adopted by o<strong>the</strong>r countries have been used (Table 4.8).<br />

Data supplied by <strong>the</strong> Mussel Watch Programme (Figure 4.10) show that concentrations <strong>of</strong><br />

Lead in mussels at <strong>the</strong> monitored sites are consistently above guideline limits for foodstuffs over <strong>the</strong><br />

period 1997–2007, while concentrations <strong>of</strong> Cadmium frequently exceed <strong>the</strong>se limits, and those for<br />

Zinc do so occasionally. Concentrations <strong>of</strong> Copper are, however, well below specified levels (Table<br />

4.8). No clear trends over time are evident for any <strong>of</strong> <strong>the</strong> trace metals, although recent data (post<br />

2007) are lacking.<br />

Concentrations <strong>of</strong> Lead in mussels from Saldanha <strong>Bay</strong> tend to be consistently high at <strong>the</strong><br />

TNPA site (at <strong>the</strong> base <strong>of</strong> <strong>the</strong> iron ore terminal on <strong>the</strong> Small <strong>Bay</strong> side, values generally greater than<br />

60 ppm), occasionally spiking to very high level at this site (715 ppm in Oct 2001), but tend to be<br />

lower at <strong>the</strong> o<strong>the</strong>r sites (mostly below 10 ppm), although <strong>the</strong>y occasionally spike to high levels at<br />

<strong>the</strong>se sites as well (e.g. 250 ppm at <strong>the</strong> mussel rafts site at <strong>the</strong> base <strong>of</strong> <strong>the</strong> Marcus Island causeway).<br />

Compared with <strong>the</strong> guideline limit <strong>of</strong> 0.5 ppm <strong>the</strong>se levels are extremely high and are very<br />

concerning. These high levels <strong>of</strong> Lead in are almost certainly linked to <strong>the</strong> export <strong>of</strong> Lead ore from<br />

<strong>the</strong> multipurpose quay, which is situated in close proximity to <strong>the</strong> TNPA site. Levels <strong>of</strong> Cadmium in<br />

mussels from Saldanha <strong>Bay</strong> are less variable than Lead and appear to be <strong>of</strong> a similar magnitude at all<br />

sites (mostly between 1-10 ppm) but occasionally exceed this level. Relative to guideline levels this<br />

is very high and is also cause for concern for anyone who may be consuming <strong>the</strong>se mussels. Levels<br />

<strong>of</strong> Zinc are mostly within <strong>the</strong> range <strong>of</strong> 50-200 ppm but occasionally have been observed to spike to<br />

levels as high as 400 ppm or more which is way in excess <strong>of</strong> <strong>the</strong> guideline limit <strong>of</strong> 150 ppm listed by<br />

<strong>the</strong> Canadian authorities (Table 4.8).<br />

Rights holders engaged in bivalve culture (mussels and oysters) in South Africa are also<br />

required to report on concentrations in harvested organisms on an annual basis. Data were<br />

obtained for three trace metal indicators (Cadmium, Lead and Mercury) for three farms (Blue <strong>Bay</strong><br />

Aquafarm, West Coast Aquaculture, West Coast Oyster Growers and Striker Fishing) in Saldanha <strong>Bay</strong><br />

covering <strong>the</strong> period 1993-2010 (Figure 4.10). Data from <strong>the</strong>se farms suggest that <strong>the</strong> situation in <strong>the</strong><br />

deeper parts <strong>of</strong> <strong>the</strong> <strong>Bay</strong> where <strong>the</strong> farms are located is less <strong>of</strong> a problem than in <strong>the</strong> case with <strong>the</strong><br />

nearshore coastal water where <strong>the</strong> Mussel Watch programme samples are collected.<br />

Concentrations <strong>of</strong> Lead were consistently above guideline levels in <strong>the</strong> period prior to 2000, albeit<br />

nowhere near as high as for <strong>the</strong> nearshore mussel samples (never more than 3 ppm), but since this<br />

time have been mostly within guideline limits (i.e. less than 0.5 ppm). Concentrations <strong>of</strong> Mercury in<br />

<strong>the</strong> mussel flesh from <strong>the</strong> farms has also mostly been within guideline limits (i.e. less than 0.5 ppm),<br />

apart from one or two spikes above this level (maximum concentration recorded = 1.7 ppm in 1994).<br />

Concentrations <strong>of</strong> Cadmium have always been within guideline limits (

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