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parks victoria technical series marine natural values study vol 2 ...

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Parks Victoria Technical Series No. 79<br />

Flinders and Twofold Shelf Bioregions Marine Natural Values Study<br />

Table 22. Summary of the number of species in major biotic groups from surveys in Cape Howe<br />

Marine National Park.<br />

Biotic group<br />

Number of species<br />

Macrophytes 59<br />

Green algae 3<br />

Brown algae 13<br />

Red algae 39<br />

Seagrasses 4<br />

Invertebrates 57<br />

Decapod crustaceans 14<br />

Chitons 1<br />

Gastropods 27<br />

Sea slugs 3<br />

Cephalopods 1<br />

Echinoderms 11<br />

Vertebrates 124<br />

Fish 40<br />

Birds 63<br />

Reptiles 5<br />

Mammals 6<br />

Intertidal<br />

Soft sediment<br />

As noted by Plummer et al. (2003) no specific data on the biota on sandy beaches are<br />

available in the MNP or nearby. Intertidal soft sediment flora is restricted to macroalgae drift<br />

and macroalgal epiphytes. Beach-washed materials in sandy beach habitats are a significant<br />

source of food for many shore birds, and contribute to the detrital cycle that nourishes many<br />

of the invertebrates, such as bivalves, living in the sand (Parks Victoria 2006c).<br />

Reef<br />

Rocky intertidal reefs, also called rocky reefs or intertidal platforms, are generally found in<br />

Victoria on and near headlands with stretches of sandy beaches either side. Along with<br />

beaches, intertidal reefs are one of the most accessible components of the <strong>marine</strong><br />

environment as they are the interface between the ocean and the land (Power and Boxshall<br />

2007). As such they are valued as important habitats by people and tend to be visited more<br />

than other sections of the coast (Carey et al. 2007a; Carey et al. 2007b). This means they<br />

are often subjected to human pressures like harvesting, fossicking and trampling as well as<br />

pressures from pollution sources on land and in the sea (Power and Boxshall 2007).<br />

Intertidal reef biota are exposed to large changes in physical conditions such as temperature<br />

and desiccation. There is great spatial and temporal variability in the life histories of the<br />

organisms and the environmental processes in reef habitats (Underwood and Chapman<br />

2004). The recruitment of new biota onto the reef, from the plankton, strongly influences the<br />

ecological patterns for individual species and assemblages. Interactions between biota on<br />

the reef also influence biota distribution. Resources which are often in short supply on<br />

intertidal reefs are space on which to live and the food itself (Underwood and Chapman<br />

2004). The remote location of the MNP means that human threats to the intertidal reef such<br />

as biota collection and trampling is low, due to this there is has been no intertidal reef<br />

monitoring program in Cape Howe MNP.<br />

Macroalgae and Aggregating Sessile Invertebrates<br />

The dominant intertidal algae in Cape Howe MPA are sea lettuce Ulva australis, neptune’s<br />

necklace Hormosira banksii and various coralline red algae (Plummer et al. 2003). The bull<br />

76

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