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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 />

List <strong>of</strong> Figures<br />

Figure 5.5.<br />

Figure 5.6.<br />

Figure 5.7.<br />

Figure 5.8.<br />

Figure 5.9.<br />

Figure 5.10.<br />

Figure 6.1.<br />

Figure 6.2.<br />

Figure 6.3.<br />

Figure 6.4<br />

Figure 6.5.<br />

Figure 6.6<br />

Figure 6.7<br />

and blue lines) is indicative <strong>of</strong> improving water quality, while an upward slope in<br />

<strong>the</strong>se lines in indicative <strong>of</strong> decreasing water quality. .............................................. 68<br />

Faecal coliform and E. coli logarithmic counts at 4 sampling stations within Big <strong>Bay</strong><br />

(Feb 1999-Feb 2012). A Downward slope <strong>of</strong> <strong>the</strong> regression (solid red and blue<br />

lines) is indicative <strong>of</strong> improving water quality, while an upward slope in <strong>the</strong>se lines<br />

in indicative <strong>of</strong> decreasing water quality. ................................................................. 69<br />

Faecal coliform and E. coli logarithmic counts at 3 sampling stations within<br />

Langebaan Lagoon (Feb 1999-Feb 2012). A Downward slope <strong>of</strong> <strong>the</strong> regression<br />

(solid red and blue lines) is indicative <strong>of</strong> improving water quality, while an upward<br />

slope in <strong>the</strong>se lines in indicative <strong>of</strong> decreasing water quality. ................................. 70<br />

Faecal coliform and E. coli logarithmic counts at 3 sampling stations within<br />

Langebaan Lagoon (Feb 1999-Feb 2012). A Downward slope <strong>of</strong> <strong>the</strong> regression<br />

(solid red and blue lines) is indicative <strong>of</strong> improving water quality, while an upward<br />

slope in <strong>the</strong>se lines in indicative <strong>of</strong> decreasing water quality. ................................. 71<br />

An illustration <strong>of</strong> <strong>the</strong> proposed routine monitoring programme to be trialled in<br />

South Africa. Source: South African Water Quality Guidelines for Coastal Marine<br />

Waters (RSADEA <strong>2011</strong>). ............................................................................................ 73<br />

Trace metal concentrations in mussels collected from five sites in Saldanha <strong>Bay</strong> as<br />

part <strong>of</strong> <strong>the</strong> Mussel Watch Programme. (Source <strong>of</strong> data: G. Kiviets, Marine and<br />

Coastal Management, Department <strong>of</strong> <strong>Environmental</strong> Affairs and Tourism).<br />

Recommended maximum limits for trace metals in seafood as stipulated in South<br />

African legislation are shown as a dotted red line. .................................................. 78<br />

Concentrations <strong>of</strong> Cadmium, Lead and Mercury in mussels and oysters from four<br />

bivalve culture operations in Saldanha <strong>Bay</strong> covering <strong>the</strong> period 1993 to 2010.<br />

Recommended maximum limits for trace metals in seafood as stipulated in South<br />

African legislation are shown as a dotted red line. .................................................. 79<br />

A) Under natural circumstances, dune vegetation can “move” with <strong>the</strong> beach as it<br />

erodes and accrete under <strong>the</strong> influence <strong>of</strong> natural processes. B) Protection <strong>of</strong><br />

infrastructure erected too close to <strong>the</strong> high water mark, on <strong>the</strong> o<strong>the</strong>r hand,<br />

necessitates construction <strong>of</strong> artificial barriers and leads to <strong>the</strong> loss <strong>of</strong> <strong>the</strong> beach<br />

ecosystem and associated amenities. ...................................................................... 83<br />

Graph showing <strong>the</strong> relative change in area over time for Spreeuwalle and<br />

Langebaan Beach (1960 – 2012). .............................................................................. 84<br />

Spreeuwalle beach showing <strong>the</strong> position <strong>of</strong> <strong>the</strong> transect line in <strong>the</strong> middle <strong>of</strong> <strong>the</strong><br />

beach (Source: Gericke 2012). .................................................................................. 84<br />

Variation in beach width across a transect <strong>of</strong> <strong>the</strong> central section <strong>of</strong> Spreeuwalle<br />

beach (Source: Gericke 2012). .................................................................................. 85<br />

Rock revetments constructed along <strong>the</strong> beach at Langebaan in an effort to protect<br />

coastal infrastructure. .............................................................................................. 86<br />

Groyne construction site Langebaan north beach. 1st groyne is completed and<br />

position <strong>of</strong> 2nd groyne is show in white. Area A and B are sand “slurry” sites (see<br />

text for explanation). Area C sand dredging site for beach reclamation. Source:<br />

Prestedge Retief Dresner Wijnberg. ......................................................................... 87<br />

<strong>State</strong> <strong>of</strong> <strong>the</strong> beach north <strong>of</strong> Groyne 2 in May 2010. (view looking south from <strong>the</strong><br />

middle <strong>of</strong> Leentjiesklip 1 beach towards <strong>the</strong> groyne) .............................................. 88<br />

viii<br />

ANCHOR<br />

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

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