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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 />

outside the MPAs. They found there was no significant difference in species richness and<br />

number of species between MPA and reference sites post-declaration for the Twofold Shelf<br />

bioregion. Limitations to this work include the relatively short time since declaration and the<br />

corresponding small data set (Keough and Carnell 2009). All algae analysed had similar<br />

percentage cover between MPA and reference sites (Keough and Carnell 2009). The purple<br />

sea urchin Heliocidaris erythrogramma and dogwelk Dicathais orbita showed a greater<br />

abundance at reference sites compared to MPA sites (Keough and Carnell 2009). The triton<br />

Cabestana spengleri, red bait crab Plagusia chabrus and H. erythrogramma had significant<br />

differences in abundance between the various MPAs (Keough and Carnell 2009). The<br />

abundance of dominant fish species varied, but were generally similar between MPA and<br />

reference sites over time (Keough and Carnell 2009). Mado, purple wrasse and bluethroated<br />

wrasse were particularly variable but differences were not related to MPAs (Keough<br />

and Carnell 2009). A clear MPA effect is unlikely to be detected until sometime after<br />

declaration. Nationally and internationally it has taken well over a decade since declaration<br />

to detect changes in fauna size classes and abundance in MPAs (Edgar et al. 2009; Edgar<br />

and Stuart-Smith 2009). A major benefit of MPA declaration, apart from recovery from fishing<br />

pressure, is to ensure the protection of the MNP area against future threats to biodiversity<br />

and <strong>natural</strong> processes.<br />

A targeted analysis of monitoring data in relation to conservation outcomes for the park will<br />

be done by 2013. The subtidal reef monitoring program will continue to be implemented in<br />

Cape Howe MNP. The major directions for monitoring include implementing an expanded<br />

and improved monitoring program following a review of the major findings taking into<br />

account knowledge generated since park declaration and conservation outcomes developed<br />

for the MNPs (Keough et al. 2007; Power and Boxshall 2007; Keough and Carnell 2009)<br />

Other ongoing research in Cape Howe MNP includes research being conducted by the<br />

University of Melbourne trialling options for improving management of illegal activities in the<br />

MNP.<br />

Statewide, the Museum of Victoria is collecting additional data on the <strong>marine</strong> <strong>natural</strong> <strong>values</strong><br />

of Victoria’s MPAs. They are gathering information about <strong>natural</strong> history through video and<br />

photos, and using semi-quantitative methods to determine spatial and temporal changes<br />

across the system in response to threats, including <strong>marine</strong> pests and climate change. Jan<br />

Carey, University of Melbourne, is conducting research focussing on <strong>marine</strong> pest species<br />

which may impact on park <strong>values</strong>, and the MPAs which are most at risk of invasion. This will<br />

help prioritise Parks Victoria surveillance monitoring efforts to MPAs where there is greatest<br />

potential for successful management.<br />

2.4.7 KNOWLEDGE GAPS<br />

No new surveys exist for the ecological communities of sandy beaches, intertidal soft<br />

sediments. No information exists at present for water column assemblages. Major threats<br />

have been identified for Cape Howe MNP but we have limited knowledge of the effect on the<br />

<strong>natural</strong> <strong>values</strong>, particularly ecological communities.<br />

88

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