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Parks Victoria Technical Series No. 79<br />

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

Cape Howe MNP is thought to be an important feeding area for several threatened bird<br />

species (Parks Victoria 2006c; Carey et al. 2007b). This includes the endangered<br />

Australasian bittern Botaurus poiciloptilus, critically endangered grey-tailed tattler<br />

Heteroscelus brevipes, and the endangered wandering albatross Diomedea exulans. All of<br />

which are listed under the Flora and Fauna Guarantee (FFG) Act (1998) with the wandering<br />

albatross also listed under the Commonwealth Environment Protection and Biodiversity<br />

Conservation (EPBC) Act (1999). The MNP protects feeding areas for bird species that are<br />

listed under the Japan–Australia Migratory Bird Agreement (JAMBA) and the China–<br />

Australia Migratory Bird Agreement (CAMBA). It is also an important foraging area for a<br />

significant breeding colony of little penguins Eudyptula minor from neighbouring Gabo Island<br />

(Plummer et al. 2003).<br />

The conservation listed southern right Eubalaena australis and humpback whales Megaptera<br />

novaeangliae, and leatherback Dermochelys coriacea, green Chelonia mydas and hawksbill<br />

turtles Eretmochelys imbricata use the MNP waters (Parks Victoria 2006c). The southern<br />

right whale E. australis has been observed to calf in the park but is not known to feed there.<br />

The state vulnerable New Zealand fur seal Arctophoca forsteri has also been recorded<br />

breeding in the MNP. The killer whale Orcinus orca, minke whale Balaenoptera acutorostrata<br />

and Australian fur seal Arctocephalus pusillus doriferus have been observed in the waters in<br />

and around the park.<br />

Serious threats to the Cape Howe MNP include limited ecological knowledge of important<br />

processes. Poaching of abalone, invasive <strong>marine</strong> pests from commercial and recreational<br />

boats; anchor damage; and climate change all pose serious threats to the integrity of the<br />

MNP (Carey et al. 2007b). Measures to address or minimise these threats form part of the<br />

management plan for Cape Howe MNP (Parks Victoria 2006c). Ongoing intertidal and<br />

subtidal reef monitoring, and specific research aims to increase ecological knowledge about<br />

the <strong>natural</strong> <strong>values</strong> of, and threats to Cape Howe MNP.<br />

2.4.1 PHYSICAL PARAMETERS & PROCESSES<br />

Cape Howe MNP is 4060 hectares in size which makes it the fourth largest of the 24 Marine<br />

National Parks or Sanctuaries in Victoria (Table 21, Figure 30). Its shoreline geology<br />

consists of predominately large mobile dunes with sandy beaches, and boulder strewn<br />

outcrops of sandstone in the east (Bird 1993). Water depths reach 105 m (Holmes et al.<br />

2007b). Greater than 85 % of the MNP is > 20 m depth. Prevailing winds and swells are<br />

generally from the south-west and north-east. The coastline is influenced by high-energy<br />

waves and swells. Weather originating from the south-west and east influences water activity<br />

and movement, as do twice-daily tides (Parks Victoria 2006c). The warm water East<br />

Australian Current is a major influence in the MNP (Parks Victoria 2006c). As the continental<br />

shelf is quite close to the far eastern Victorian shore, cold water upwellings are frequent and<br />

mix with the warmer waters, bringing increased nutrients and creating an ecosystem high in<br />

productivity (Parks Victoria 2006c; Edmunds et al. 2010a). A small intermittent estuary, the<br />

outflow from Lake Wau Wauka, runs directly into the park (Table 21). The catchment<br />

adjacent to the MNP is the remote and relatively undisturbed Cape Howe Wilderness Zone<br />

which is part of Croajingolong National Park.<br />

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