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 />
Recommendations<br />
12.8 Summary <strong>of</strong> environmental monitoring requirements<br />
In summary, <strong>the</strong> environmental monitoring currently implemented in Saldanha <strong>Bay</strong> and Langebaan<br />
Lagoon (e.g. sediment, benthic macr<strong>of</strong>auna and birds) should continue with some small adjustments<br />
or additions, however, monitoring <strong>of</strong> o<strong>the</strong>r environmental parameters that are not currently<br />
assessed on a regular basis (e.g. temperature, oxygen, rocky intertidal and fish populations) require<br />
structured, maintained monitoring to be implemented.<br />
Table 11.1. Tabulated summary <strong>of</strong> <strong>Environmental</strong> parameters reported on in <strong>the</strong> <strong>State</strong> <strong>of</strong> <strong>the</strong> <strong>Bay</strong>: Saldanha<br />
<strong>Bay</strong> and Langebaan Lagoon.<br />
Parameter monitored Time period Anthropogenic induced impact<br />
Water Quality<br />
Physical<br />
aspects 1974-2000 No clear change attributable to development<br />
(temperature, salinity,<br />
dissolved oxygen, nutrients<br />
and chlorophyll)<br />
Current circulation patterns<br />
and current strengths<br />
1977 vs. 1991 Reduced wave energy, and impaired circulation<br />
and rate <strong>of</strong> exchange in Small <strong>Bay</strong><br />
Increased current strength alongside obstructions<br />
(e.g. ore terminal)<br />
Microbiological (faecal 1999-<strong>2011</strong> Faecal coliform counts in Small <strong>Bay</strong> frequently<br />
coliform)<br />
exceed safety levels.<br />
Big <strong>Bay</strong> and Langebaan Lagoon mostly remain<br />
within safety levels for faecal coliform pollution<br />
Heavy metal contaminants<br />
in water<br />
1997-2008 Concentrations <strong>of</strong> cadmium, copper, lead, zinc,<br />
iron and manganese in mussel flesh currently well<br />
below required safety levels, but this may change<br />
following any future dredging events owing to<br />
elevated metal concentration in sediments.<br />
SEDIMENTS<br />
Particle<br />
(mud/sand/gravel)<br />
size<br />
Particulate Organic Carbon<br />
(POC)<br />
Particulate Organic Nitrogen<br />
(PON)<br />
Trace metal contaminants<br />
in sediments<br />
1977-<strong>2011</strong> Mud component <strong>of</strong> sediments has increased as a<br />
result <strong>of</strong> reduced water movement and dredging<br />
(negative impact) but has recovered somewhat<br />
since <strong>the</strong> last major dredging events (1999 and<br />
2007).<br />
1974-<strong>2011</strong> Elevated levels <strong>of</strong> POC evident at Yacht Club basin<br />
and Mussel Farm (negative impacts). POC<br />
increased in 2008-2009 at Multi-Purpose Terminal<br />
and Yacht Club basin.<br />
1974-2010 PON concentrations have increased steadily over<br />
time in Yacht Club basin and at multipurpose quay.<br />
PON concentrations remain low in Big <strong>Bay</strong>.<br />
1980-<strong>2011</strong> Cadmium, lead, copper and nickel are currently<br />
elevated considerably above historic levels.<br />
Concentrations were highest in 1999 following<br />
major dredge event. Pb, Cu, Ni elevated in 2008-<br />
2010 at Yacht Club and multipurpose terminal,<br />
which may be related to maintenance dredging<br />
that occurred at end 2007/beginning 2008.<br />
252<br />
ANCHOR<br />
e n v i r o n m en t a l