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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 />

Intertidal invertebrates<br />

This would explain why firstly Mytilus cover reduced, i.e. removed by wave action, and secondly A.<br />

ater cover is recorded, i.e. only now visible and recordable with non-destructive methods.<br />

Invasive alien species have been identified as one <strong>of</strong> <strong>the</strong> major threats to <strong>the</strong> maintenance <strong>of</strong><br />

biodiversity in <strong>the</strong> marine environment (Carlton & Geller 1993, Carlton 1999, Ruiz et al. 1999, IUCN<br />

2009), particularly in <strong>the</strong> context <strong>of</strong> global climate change (Occhipinti-Ambrogi 2007, Occhipinti-<br />

Ambrogi & Galil 2010). To date, 22 confirmed extant marine aliens, plus 18 cryptogenic species, have<br />

been recorded from South African waters, with one additional species found in on-land mariculture<br />

facilities (Griffiths et al. 2009). The true number <strong>of</strong> introduced species may well exceed <strong>the</strong>se<br />

estimates by several times. The major means <strong>of</strong> introduction is international shipping, i.e. via ballast<br />

water and as attachment to <strong>the</strong> hulls <strong>of</strong> ships, followed by aquaculture (Galil et al. 2008). Saldanha<br />

<strong>Bay</strong> is a deepwater harbour receiving vessels from all over <strong>the</strong> world and it thus likely that one <strong>of</strong> <strong>the</strong><br />

greatest perils to <strong>the</strong> intertidal (and in fact all o<strong>the</strong>r) communities in Saldanha <strong>Bay</strong> is <strong>the</strong> introduction<br />

<strong>of</strong> alien species, and <strong>the</strong>ir potential to become invasive.<br />

8.4 SUMMARY OF FINDINGS<br />

A total <strong>of</strong> 84 taxa were recorded from <strong>the</strong> eight study sites, most <strong>of</strong> which had also been found in <strong>the</strong><br />

previous survey years. The faunal component was represented by 16 species <strong>of</strong> grazers, 3 trappers, 7<br />

predators and scavengers, 6 anemones, and 18 filter-feeders. The algal component comprised 22<br />

corticated (foliose) seaweeds, 6 ephemerals, 1 kelp, 4 crustose (or encrusting) corallines and 1<br />

articulated coralline. The species are generally common to <strong>the</strong> South African West Coast and many<br />

are listed by o<strong>the</strong>r studies conducted in <strong>the</strong> Saldanha <strong>Bay</strong> area including <strong>the</strong> two alien invasive<br />

species, <strong>the</strong> Mediterranean mussel Mytilus galloprovincialis and <strong>the</strong> North American acorn barnacle<br />

Balanus glandula.<br />

Within a site, <strong>the</strong> vertical emersion gradient <strong>of</strong> increasing exposure to air leads to a clear<br />

zonation <strong>of</strong> flora and fauna from low shore to high shore. Differences among <strong>the</strong> rocky shores,<br />

however, are strongly influenced by <strong>the</strong> prevailing wave exposure at a shore as well as substratum<br />

topography. Very sheltered shores had generally low biotic cover consisting primarily <strong>of</strong> grazers and<br />

trappers, with minor cover <strong>of</strong> sessile filter feeders and encrusting algae. With increasing wave force,<br />

filter feeders were clearly <strong>the</strong> most important group. The two very sheltered boulder beaches in<br />

Small <strong>Bay</strong> separate from <strong>the</strong> flat Schaapen Island sites, which may also be related to geographic<br />

location as Schaapen Island lies in a transitional zone between <strong>the</strong> <strong>Bay</strong> and <strong>the</strong> Lagoon, and to <strong>the</strong><br />

nutrient input through seabird guano that favours algal growth on Schaapen Island. Similarly, <strong>the</strong><br />

steep boulder beach Iron Ore Terminal separates from <strong>the</strong> o<strong>the</strong>r more flattish semi-exposed to<br />

exposed sites.<br />

From <strong>the</strong> temporal pattern displayed by <strong>the</strong> rocky shore communities, it is evident that at<br />

none <strong>of</strong> <strong>the</strong> sites <strong>the</strong>re is a directional change in community composition that would indicate a<br />

persistent change, such as for example <strong>the</strong> arrival or loss <strong>of</strong> a species. Ra<strong>the</strong>r <strong>the</strong> communities show<br />

temporal fluctuations, reflecting <strong>the</strong> temporary dominance <strong>of</strong> short-lived ephemeral species and/or<br />

interannual variation in larval supply or recruitment success. In general, rocky shore communities<br />

were relatively stable with only minor changes over <strong>the</strong> years.<br />

The two most important filter feeders, being also <strong>the</strong> characteristic species at most shores<br />

and zones, are <strong>the</strong> aliens M. galloprovincialis and B. glandula. The latter is most abundant at mid<br />

shores <strong>of</strong> semi-exposed sites, but rarer at exposed sites and low shores. M. galloprovincialis, on <strong>the</strong><br />

o<strong>the</strong>r hand, fares best at wave-exposed sites and lower down <strong>the</strong> shore. It is likely that one <strong>of</strong> <strong>the</strong><br />

greatest threats to rocky shore communities in Saldanha <strong>Bay</strong> is <strong>the</strong> introduction <strong>of</strong> alien species via<br />

shipping, and <strong>the</strong>ir potential to become invasive.<br />

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ANCHOR<br />

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

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