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
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<strong>State</strong> <strong>of</strong> Saldanha <strong>Bay</strong> & Langebaan Lagoon <strong>2011</strong><br />
Water quality<br />
4.4 Summary <strong>of</strong> Water Quality in Saldanha <strong>Bay</strong> and Langebaan Lagoon<br />
There are no long term trends evident in <strong>the</strong> water temperature, salinity and dissolved oxygen data<br />
series that solely indicate anthropogenic causes. In <strong>the</strong> absence <strong>of</strong> actual discharge <strong>of</strong> industrially<br />
heated sea water into <strong>the</strong> <strong>Bay</strong>, water temperature is unlikely to show any change that is discernable<br />
from that imposed by natural variability. Admittedly <strong>the</strong>re is limited pre-development data (pre<br />
1975), so although it is conceivable that construction <strong>of</strong> <strong>the</strong> causeway and ore/oil Terminal has<br />
impeded water flow thus increasing residence time and increasing water temperatures, salinity and<br />
likely decreasing oxygen concentration, particularly in Small <strong>Bay</strong>, <strong>the</strong>re is little data to support this.<br />
Given that cold, nutrient rich water influx during summer is density driven; dredging shipping<br />
channels could have facilitated this process which would be evident as a decrease in water<br />
temperature and salinity and an increase in nitrate and chlorophyll concentrations. Once again<br />
<strong>the</strong>re is little evidence <strong>of</strong> this in <strong>the</strong> available data series. Natural, regional oceanographic processes<br />
(wind driven upwelling or downwelling and extensive coast–<strong>Bay</strong> exchange) ra<strong>the</strong>r than internal,<br />
anthropogenic causes, appear to remain <strong>the</strong> major factors affecting physical and chemical water<br />
characteristics in Saldanha <strong>Bay</strong>. The construction <strong>of</strong> physical barriers (<strong>the</strong> iron ore/oil Terminal and<br />
<strong>the</strong> Marcus Island causeway) do appear to have changed current strengths and circulation within<br />
Small <strong>Bay</strong>, resulting in increased residence time (decreased flushing rate), enhanced clockwise<br />
circulation and enhanced boundary flows. There has also been an increase in sheltered and semisheltered<br />
wave exposure zones in both Small and Big <strong>Bay</strong> subsequent to harbour development.<br />
The microbiological monitoring program provides evidence that while many <strong>of</strong> <strong>the</strong><br />
monitoring sites in Small <strong>Bay</strong> still have faecal coliform counts in excess <strong>of</strong> <strong>the</strong> safety guidelines for<br />
both mariculture and recreational use, <strong>the</strong>re is a trend <strong>of</strong> improving compliance at many sites for<br />
which <strong>the</strong> relevant authorities should be commended. However, <strong>the</strong> situation in Small <strong>Bay</strong> remains<br />
a concern, with many sites exceeding levels for safe recreational activities. Given <strong>the</strong> current<br />
importance and likely future growth <strong>of</strong> both <strong>the</strong> mariculture and tourism industries within Saldanha<br />
<strong>Bay</strong>, it is imperative that whatever efforts have been taken in recent years (e.g. upgrading <strong>of</strong> sewage<br />
and storm water facilities to keep pace with development and population growth) to combat<br />
pollution by faecal coliforms in Small <strong>Bay</strong> should be increased and applied more widely. Continued<br />
monitoring <strong>of</strong> bacterial indicators (intestinal Enterococci in particular), to assess <strong>the</strong> effectiveness <strong>of</strong><br />
adopted measures, is also required and should be undertaken at all sites on a bimonthly basis.<br />
Large volumes <strong>of</strong> ballast water are discharged into Saldanha <strong>Bay</strong> on an annual basis. This<br />
poses an enormous risks in respect <strong>of</strong> <strong>the</strong> introduction <strong>of</strong> alien species as well as contaminants in <strong>the</strong><br />
ballast water (trace metals, E. coli, etc.). Compliance with ballast water treatment requirements<br />
(e.g. open ocean exchange, on-board treatment systems) designed to minimize <strong>the</strong> risks <strong>of</strong> alien<br />
introductions should be rigorously enforced and voluntary compliance with any additional measures<br />
strongly encouraged.<br />
Data supplied by <strong>the</strong> Mussel Watch Programme (DEA) and mariculture operators in Saldanha<br />
<strong>Bay</strong> suggest that concentrations <strong>of</strong> trace metals are high along <strong>the</strong> shore (particularly for Lead near<br />
<strong>the</strong> multipurpose quay) and frequently or even consistently (in <strong>the</strong> case <strong>of</strong> Lead) above published<br />
guidelines for foodstuff, concentrations <strong>of</strong>fshore are clearly much lower and less <strong>of</strong> a concern. High<br />
concentrations <strong>of</strong> trace metals along <strong>the</strong> shore is very clearly <strong>of</strong> concern and points to <strong>the</strong> need for<br />
management intervention that can address this issue as it poses a very clear risk to <strong>the</strong> health <strong>of</strong><br />
people harvesting mussels from <strong>the</strong> shore. Regrettably no new data have been available from this<br />
programme since 2007.<br />
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