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Parks Victoria Technical Series No. 79<br />

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

Figure 27. Finger sponges and colonial sea squirt in Point Hicks Marine National Park. Photo by Mark<br />

Norman, Museum of Victoria.<br />

A number of other introduced <strong>marine</strong> pests also have the potential to colonise the park,<br />

especially in the sheltered waters of Stable Bay and the western side of Point Hicks (Parks<br />

Victoria 2006f). The park is vulnerable to pest introductions from ballast water and biofouling<br />

because of shipping lanes (Parks Victoria 2006f). Recreational vessels and users are also<br />

potential vectors for exotic species and diseases (e.g. from contaminated diving equipment)<br />

(Parks Victoria 2006f). Impacts from introduced <strong>marine</strong> pests are as diverse as the species<br />

themselves and include altering <strong>natural</strong> nutrient cycles and outcompeting native species for<br />

food and or space. Introduced <strong>marine</strong> pests can have economic impacts (e.g. commercial<br />

fisheries) and social impacts (e.g. affect public health and safety) (Parks Victoria 2006f).<br />

A virus affecting abalone called abalone viral ganglioneuritus has been slowly spreading<br />

east along Victoria’s west coast. This virus can kill a large percentage of abalone in an area<br />

and has been confirmed from Discovery Bay MNP to near Cape Otway (DPI 2009). It is not<br />

in the Point Hicks MNP but its spread into the park could have serious long term ecological<br />

consequences for rocky reef communities (DPI 2009).<br />

Climate change represents a serious threat to <strong>marine</strong> ecosystems (McLeod et al. 2009) but<br />

specific ecological consequences of accelerating climate change are not well understood in<br />

<strong>marine</strong> systems, particularly in temperate systems. Climate change is predicted to increase<br />

water temperature, alter chemical composition (salinity, acidity and carbonate saturation),<br />

change circulation and productivity, increase frequencies of extreme weather events and<br />

exposure to damaging ultraviolet light (UVB), and increase air temperature, cloud cover and<br />

sea levels (conservatively 80 cm by 2100; CSIRO-BoM 2007; Fine and Franklin 2007; VCC<br />

2008; McLeod et al. 2009). A combined increase in cloud cover and sea level could result in<br />

decreased light availability potentially changing benthic flora. Increased storm surges and<br />

ocean current changes also have the potential to change the distribution of fauna and flora<br />

and could result in loss of habitats (CSIRO-BoM 2007). Intertidal communities will face<br />

63

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