the reef biota at bunurong marine national park - Parks Victoria
the reef biota at bunurong marine national park - Parks Victoria
the reef biota at bunurong marine national park - Parks Victoria
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<strong>Parks</strong> <strong>Victoria</strong> Technical Series No. 84<br />
Bunurong Subtidal Reef Monitoring<br />
3.5 Fishing<br />
Abalone<br />
The average size of blacklip abalone, H. rubra, was similar between <strong>the</strong> Bunurong MNP and<br />
<strong>the</strong> reference areas during most surveys prior to 2006, with vari<strong>at</strong>ions in mean size generally<br />
less than 5 mm length (Figure 3.23a). A marked decrease in mean size of H. rubra was<br />
measured both inside and outside <strong>the</strong> MNP between 2006 and 2011, with mean size falling<br />
to well below previously observed sizes (Figure 3.23a). The proportion of legal sized abalone<br />
has also declined during this period to lowest observed levels, both inside and outside <strong>the</strong><br />
MNP (Figure 3.24). Although a decline was also evident in MNP sites <strong>the</strong> scale of decline,<br />
and low abundances (Figure 3.23b), suggests an increased in fishing pressure in Western<br />
reference sites, which may extend into <strong>the</strong> MNP, to a lesser extent.<br />
Rock Lobster<br />
The sou<strong>the</strong>rn rock lobster J. edwardsii is common inside <strong>the</strong> MNP, however <strong>the</strong> survey sites<br />
do not encompass <strong>the</strong>ir preferred microhabit<strong>at</strong> and do <strong>the</strong>refore do not adequ<strong>at</strong>ely survey<br />
<strong>the</strong>ir abundances (Figure 3.25).<br />
Fishes<br />
The size spectrum analysis indic<strong>at</strong>es th<strong>at</strong> in reference sites <strong>the</strong> abundance of larger fishes in<br />
2006 and 2010 were amongst <strong>the</strong> lowest of all surveys, 2010 was also <strong>the</strong> lowest for sites<br />
within <strong>the</strong> MNP (Figure 3.26). The biomass and density of fishes above 200 mm length in<br />
2006, 2010 and 2011 is also <strong>the</strong> lowest of recorded observ<strong>at</strong>ions inside <strong>the</strong> MNP. Similarly<br />
observ<strong>at</strong>ions of biomass and density of fishes above 200 mm length <strong>at</strong> reference sites were<br />
low in 2010 and 2011 (Figure 3.27 and Figure 3.28). A decline in size of <strong>the</strong> larger, fished<br />
species, including blue thro<strong>at</strong>ed wrasse N. tetricus, sen<strong>at</strong>or wrasse P. l<strong>at</strong>iclavius and magpie<br />
morwong C. nigripes was apparent (Figure 3.29 to Figure 3.31). Mean size of purple wrasse<br />
N. fucicola was rel<strong>at</strong>ively consistent across all surveys, however no N.fucicola were observed<br />
within MNP sites in 2011 (Figure 3.32).<br />
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