the reef biota at Wilsons promontory marine national - Parks Victoria

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Parks Victoria Technical Series #74SRMP Wilsons Promontory MNP2.3.5. Climate ChangeSpecies CompositionClimate change is likely to cause changes to current strengths and circulation patterns whichaffect both the ambient temperature regime and the dispersion and recruitment of propagulesor larvae. In Victoria, there may be increased incursions of the East Australia Current intoeastern Victoria and the South Australia Current into western Victoria and Bass Strait.Biological responses to such changes are potentially indicated by biogeographical changesin the species composition, toward that of adjacent, warmer bioregions. For this analysis,each species was assigned a nominal geographical range:• coldwater species, reflecting the ‘Maugean’ province, from approximately KangarooIsland in South Australia, around Tasmania and into southern New South Wales;• western species, reflecting the ‘Flindersian’ province, from southern WesternAustralia, along the Great Australian Bight and South Australia to western Victoria;• eastern species, reflecting the ‘Peronian’ province, encompassing New South Walesand into eastern Victoria;• southern species, including species ranging widely along the southern Australiancoast; and• northern species, including warm temperate and tropical species in Western Australiaand New South Wales and northward.The number of species and total number of individuals was calculated for the coldwater,western and eastern groups.Macrocystis pyriferaThe string kelp Macrocystis pyrifera, which includes the former species M. angustifolia(Macaya and Zuccarello 2010), is considered potentially vulnerable to climate changethrough reduced nutrient supply from drought and nutrient poorer warmer waters (Edyvane2003). The mean abundance of M. pyrifera was plotted using densities from Method 4, orcover estimates from Method 4 where density data were unavailable. M. pyrifera providesconsiderable vertical structure to reef habitats and can also attenuate water currents andwave motion. The loss of M. pyrifera habitats may reflect ecosystem functional changes.Centrostephanus rodgersiiThe range of the long-spined sea urchin, Centrostephanus rodgersii, has increasedconspicuously over the past decades (Johnson et al. 2005). This grazing species can causeconsiderable habitat modification, decreasing seaweed canopy cover and increasing thearea of ‘urchin barrens’. Abundances are determined using Method 2 and average29
Parks Victoria Technical Series #74SRMP Wilsons Promontory MNPabundances are plotted through time. The abundance of C. rodgersii are also influenced byinteractions with abalone as competitors for crevice space, Abalone divers may periodically‘cull’ urchins within a reef patch and the species is also of interest to urchin harvesters.Durvillaea potatorumThe bull kelp Durvillaea potatorum is a coldwater species that is likely to be vulnerable toincreased ambient temperatures. There is anecdotal evidence of a retraction of the northerndistribution down the New South Wales coast by approximately 80 km. Most of the SRMPsites specifically avoid D. potatorum habitats as these occur on highly wave-affected andturbulent reefs. Some sites contain D. potatorum stands, providing limited data on populationstatus. Durvillaea potatorum is potentially two species, having genetically andmorphologically distinct eastern and western forms (Fraser et al. 2009).2.3.6. FishingAbaloneIndicators of altered population structure from harvesting pressure on abalone were meandensity and the proportion of legal sized individuals. The size-frequency histograms werealso examined. The indicators were calculated for the blacklip abalone, Haliotis rubra, inmost regions and for the greenlip abalone, H. laevigata, where present in suitable densities(in central and western Victoria).Rock LobsterThe southern rock lobster, Jasus edwardsii, is present throughout Victoria and the easternrock lobster, Jasus verreauxi, is present in the Twofold Shelf region. The SRMP transectsgenerally did not traverse rock lobster microhabitats, however abundances and sizes arereported for suitable data.FishesPotential fishing impacts or recovery of fishing impacts within marine protected areas wereindicated by:• abundances of selected fished species;• mean size and size-frequency histograms of selected fished species;• total abundance of fishes > 200 mm length, this being the approximate legal minimumsize for most fished species;• biomass of fishes > 200 mm length, calculated using length-weight relationships; and• parameters of the size-spectra of all fishes.The size spectrum of all fishes at a site was first centred and linearised. Size frequencies foreach field size class were aggregated into classes centred on 87.5 mm (classes 1-6), 20030
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