Abstract
We analyzed and predicted spatial patterns of turnover in macroalgal community composition (beta diversity) that accounted for broad-scale environmental gradients using two contrasting community modelling methods, Generalised Dissimilarity Modelling (GDM) and Gradient Forest Modelling (GFM). Percentage cover data from underwater macroalgal surveys of subtidal rocky reefs along the southeastern coastline of continental Australia and northern coastline of Tasmania were combined with 0.01°-resolution gridded environmental variables, to develop statistical models of beta diversity. GDM, a statistical approach based on a matrix regression, and GFM, a machine learning approach based on ensemble tree based methods, were used to fit models and generate predictions of beta diversity within unsurveyed areas across the region of interest. Patterns of macroalgal beta diversity predicted by both methods were remarkably congruent and showed a similar and striking change in community composition from eastern South Australia to western Victoria and northern Tasmania. Macroalgal communities differed markedly in predicted composition between the open coast and inshore locations. A distinct algal community was predicted for the enclosed Port Philip Bay in Victoria. Sea surface temperature standard deviation and average contributed most to changes in beta diversity for both the GDM and GFM models; changes in wave exposure and oxygen also influenced beta diversity in the GDM model, while salinity and exposure contributed substantially to the GFM model. The GDM and GFM analyses allowed us to model and predict spatial patterns of beta diversity in macroalgal communities comprising >180 species over 6600 km of coastline. These outputs advance regional-scale conservation management by allowing planners to interpolate from point source ecological data to assess the distribution of biodiversity across their full domain of interest. The congruence between methods suggests that strong environmental gradients related to temperature and exposure are the common drivers of community change in this region.
Highlights
Conservation planning and management of marine biodiversity requires information on the spatial distribution of biodiversity attributes, but quantitative analysis of patterns of biodiversity are almost absent from marine systems
We modeled beta diversity based on macroalgal occurrence for a total of 185 taxa where dissimilarities between macroalgal communities occurring at survey sites were calculated using the Bray-Curtis dissimilarity
Models of beta diversity Macroalgal community composition showed a large amount of turnover, with sea surface temperate (both average and variability) playing the most important role in the Generalised Dissimilarity Modelling (GDM) model, followed by wave exposure and average oxygen concentration (Fig. 2)
Summary
Conservation planning and management of marine biodiversity requires information on the spatial distribution of biodiversity attributes, but quantitative analysis of patterns of biodiversity are almost absent from marine systems. Environmental (surrogate) data are often more readily available and cover significant geographical space, (see review by McArthur et al 2010), but have limited application when the congruence between mapped environment and biodiversity is weak or unknown (Faith 2003, Ferrier et al 2007). Such lack of congruence can cause inefficiencies and at worst, avoidable declines in biodiversity because of complacency that targets of protection are adequately safeguarded (Edgar et al 2008). Linking environmental data to spatial variation in community composition confers significant advantages over a surrogate only approach and is a highly promising strategy for cost-effective conservation prioritization and management (Arponen et al 2008)
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