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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 4.26.<br />

Figure 4.27.<br />

Figure 4.28.<br />

Figure 4.29.<br />

Figure 4.30.<br />

Figure 4.31.<br />

Figure 4.32.<br />

Figure 4.33.<br />

Monthly trends in <strong>the</strong> concentration <strong>of</strong> Ammonia Nitrate in effluent from<br />

Langebaan WWTW, June 2009 - December <strong>2011</strong>. Allowable limits as specified in<br />

terms <strong>of</strong> a General Authorisation under <strong>the</strong> National Water Act 1998 are<br />

represented by <strong>the</strong> red line. ..................................................................................... 45<br />

Monthly trends in <strong>the</strong> concentration <strong>of</strong> Nitrate Nitrogen in effluent from<br />

Langebaan WWTW, June 2009 - December <strong>2011</strong>. Allowable limits as specified in<br />

terms <strong>of</strong> a General Authorisation under <strong>the</strong> National Water Act 1998 are<br />

represented by <strong>the</strong> red line. ..................................................................................... 45<br />

Monthly trends in <strong>the</strong> concentration <strong>of</strong> Orthophosphate in effluent from<br />

Langebaan WWTW, June 2009 - December <strong>2011</strong>. Allowable limits as specified in<br />

terms <strong>of</strong> a General Authorisation under <strong>the</strong> National Water Act 1998 are<br />

represented by <strong>the</strong> red line. ..................................................................................... 46<br />

Monthly trends in <strong>the</strong> concentration <strong>of</strong> Free Active Chlorine in effluent from<br />

Langebaan WWTW, June 2009 - December <strong>2011</strong>. Allowable limits as specified in<br />

terms <strong>of</strong> a General Authorisation under <strong>the</strong> National Water Act 1998 are<br />

represented by <strong>the</strong> red line. ..................................................................................... 46<br />

Spatial extent <strong>of</strong> residential and industrial areas surrounding Saldanha <strong>Bay</strong> and<br />

Langebaan Lagoon from which storm water run<strong>of</strong>f is likely to enter <strong>the</strong> sea (areas<br />

outlined in white). Note that run<strong>of</strong>f from <strong>the</strong> Port <strong>of</strong> Saldanha and ore terminal<br />

have been excluded as it is now reportedly all diverted to storm water evaporation<br />

ponds. ....................................................................................................................... 48<br />

Location <strong>of</strong> seawater intakes and discharges for seafood processing in Saldanha<br />

<strong>Bay</strong> toge<strong>the</strong>r with location <strong>of</strong> current and proposed mariculture operations ......... 50<br />

Total monthly discharge <strong>of</strong> fresh fish processing effluent (FFP) disposed to sea by<br />

Sea Harvest from January 2001 to March 2007. ...................................................... 53<br />

Monthly trends in <strong>the</strong> numbers <strong>of</strong> Faecal coliforms in effluent from <strong>the</strong> Sea Harvest<br />

fresh fish processing effluent (FFP) discharged into Small <strong>Bay</strong> in <strong>the</strong> period Feb 201<br />

to Dec <strong>2011</strong>. .............................................................................................................. 54<br />

Figure 4.34. Allocated mariculture concession areas in Saldanha <strong>Bay</strong> 2010. .............................. 56<br />

Figure 4.35. Overall annual mussel productivity (tons) in Saldanha <strong>Bay</strong> between 2000 and 2010<br />

(source: DAFF <strong>2011</strong>) .................................................................................................. 56<br />

Figure 5.1.<br />

Figure 5.2.<br />

Figure 5.3.<br />

Figure 5.4.<br />

Schematic representation <strong>of</strong> <strong>the</strong> surface currents and circulation <strong>of</strong> Saldanha <strong>Bay</strong><br />

(A) prior to <strong>the</strong> harbour development (Pre-1973) and (B) after construction <strong>of</strong> <strong>the</strong><br />

causeway and iron-ore terminal (Present). (Adapted from Shannon and Stander<br />

1977 and Weeks et al. 1991a) .................................................................................. 58<br />

Faecal coliform and E. coli counts at 4 <strong>of</strong> <strong>the</strong> 10 sampling stations within Small <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. ................................................................. 66<br />

Faecal coliform and E. coli logarithmic counts at 3 <strong>of</strong> <strong>the</strong> 10 sampling stations<br />

within Small <strong>Bay</strong> (Feb 1999-Feb 2012). A downward slope <strong>of</strong> <strong>the</strong> regression (solid<br />

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

in <strong>the</strong>se lines in indicative <strong>of</strong> decreasing water quality............................................ 67<br />

Faecal coliform and E. coli logarithmic counts at 4 <strong>of</strong> <strong>the</strong> 10 sampling stations<br />

within Big <strong>Bay</strong> (Feb 1999-Feb 2012). A downward slope <strong>of</strong> <strong>the</strong> regression (solid red<br />

vii<br />

ANCHOR<br />

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

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