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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 />

Activities & discharges<br />

and methane which are toxic to most marine organisms (Clark, 1986). The sediments and <strong>the</strong><br />

benthic communities <strong>the</strong>y support are thus amongst <strong>the</strong> most sensitive components <strong>of</strong> coastal<br />

ecosystems to hypoxia and eutrophication (Cloern 2001). The ecological responses associated with<br />

decreasing oxygen saturation in shallow coastal systems include <strong>the</strong> initial escape <strong>of</strong> sensitive<br />

demersal fish, followed by mortality <strong>of</strong> bivalves and crustaceans, and finally mortality <strong>of</strong> molluscs,<br />

with extreme loss <strong>of</strong> benthic diversity (Vaquer-Sunyer and Duarte 2008; Howarth et al <strong>2011</strong>).<br />

Vaquer-Sunyer and Duarte (2008) propose a precautionary limit for oxygen concentrations at 4.6 mg<br />

O 2 /litre equivalent to <strong>the</strong> 90th percentile <strong>of</strong> mean lethal concentrations, to avoid catastrophic<br />

mortality events, except for <strong>the</strong> most sensitive crab species, and effectively conserve marine<br />

biodiversity.<br />

Some <strong>of</strong> <strong>the</strong> indirect consequences <strong>of</strong> an increase in phytoplankton biomass and high levels<br />

<strong>of</strong> nutrient loading are a decrease in water transparency and an increase in epiphyte grown, both <strong>of</strong><br />

which have been shown to limit <strong>the</strong> habitat <strong>of</strong> benthic plants such as seagrasses (Orth and Moore<br />

1983). Fur<strong>the</strong>rmore, <strong>the</strong>re are several studies documenting <strong>the</strong> effects that shifts in natural marine<br />

concentrations, and ratios <strong>of</strong> nitrates, phosphates and elements such ammonia and silica, have on<br />

marine organisms (Herman et al 1996; van Katwijk et al 1997; Hodgkiss and Ho 1997; Howarth et al<br />

<strong>2011</strong>). For instance, <strong>the</strong> depletion <strong>of</strong> dissolved Silica in coastal systems, as a result <strong>of</strong> nutrient<br />

enrichment, water management and <strong>the</strong> building <strong>of</strong> dams, is believed to be linked to worldwide<br />

increases in flagellate/din<strong>of</strong>lagellate species which are associated with harmful algal blooms, and are<br />

toxic to o<strong>the</strong>r biota (Hodgkiss and Ho 1997; Howarth et al <strong>2011</strong>). The toxic effect that elevated<br />

concentrations <strong>of</strong> ammonia have on plants has been documented for Zostera marina, and shows<br />

that plants held for two weeks in concentrations as low as 125 µmol start to become necrotic and<br />

die (van Katwijk et al 1997).<br />

The effects <strong>of</strong> organic enrichment, on benthic macr<strong>of</strong>auna in Saldanha <strong>Bay</strong>, have been well<br />

documented (Jackson and McGibbon 1991, Kruger 2002, Kruger et al. 2005, Stenton-Dozey 2001).<br />

Tourism and mariculture are both important growth industries in and around Saldanha <strong>Bay</strong>, and<br />

both are dependent on good water quality (Jackson and Gibbon 1991). The growth <strong>of</strong> attached<br />

algae such as Ulva sp. and Enteromorpha sp. on beaches is a common sign <strong>of</strong> sewage pollution (Clark<br />

1986). Nitrogen loading in Langebaan Lagoon associated with leakage <strong>of</strong> conservancy/septic tanks<br />

and storm water run<strong>of</strong>f has resulted in localised blooms <strong>of</strong> Ulva sp. in <strong>the</strong> past. In <strong>the</strong> summer 1993-<br />

94, a bloom <strong>of</strong> Ulva lactuca in Saldanha <strong>Bay</strong> was linked to discharge <strong>of</strong> nitrogen from pelagic fish<br />

processing plants (Monteiro et al. 1997). Dense patches <strong>of</strong> Ulva sp. are also occasionally found in<br />

<strong>the</strong> shallow embayment <strong>of</strong> Oudepos (CSIR 2002). Organic loading is a particular problem in Small<br />

<strong>Bay</strong> due to reduced wave action and water movement in this part <strong>of</strong> <strong>the</strong> <strong>Bay</strong> caused by harbour<br />

structures such as <strong>the</strong> Ore Terminal and <strong>the</strong> Causeway, as well as <strong>the</strong> multitude <strong>of</strong> organic pollution<br />

sources within this area (e.g. fish factories, mariculture farms, sewage outfalls, sewage overflow<br />

from pump stations, and storm water run<strong>of</strong>f). Langebaan Lagoon is also sheltered from wave action<br />

but strong tidal action and <strong>the</strong> shallow nature <strong>of</strong> <strong>the</strong> lagoon make it less susceptible to <strong>the</strong> long term<br />

deposition <strong>of</strong> pollutants and organic matter (Monteiro 1999 in CSIR 2002).<br />

There is one waste water treatment works (WWTW) in Saldanha and one in Langebaan. The<br />

WWTW in Saldanha disposes <strong>of</strong> treated effluent into <strong>the</strong> Bok River where it drains into Small <strong>Bay</strong><br />

adjacent to <strong>the</strong> Blouwaterbaai Resort. In addition to sewage waste, <strong>the</strong> WWTW in Saldanha also<br />

receives and treats industrial waste water from a range <strong>of</strong> industries in Saldanha:<br />

<br />

<br />

<br />

<br />

<br />

<br />

Sea Harvest<br />

Hoedtjiesbaai Hotel<br />

Protea Hotel<br />

Sou<strong>the</strong>rn Seas Fishing (not currently operation)<br />

Bongolethu Fishing Enterprises<br />

SA Lobster<br />

35<br />

ANCHOR<br />

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

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