Abstract:
The primary goals of this thesis were to understand the spatial and temporal
pattern of sponge assemblage variation over a variety of scales and investigate
suitable monitoring methods for sponge assemblages. Sponges are an
ecologically significant group in benthic marine communities, which are often
ignored in current monitoring schemes. In chapter two the sponge biodiversity
of New Zealand waters to 200m was examined using Taxonomic Distinctness
measures initially to test if genera data could be used as a proxy for species
level data in New Zealand waters. It was found that over 50% of the variation in
genera biodiversity could be explained by location and depth around New
Zealand. The study helped pinpoint where there were gaps in the New Zealand
dataset, in particular for the West Coast of the South Island and also areas such
as the Wellington South Coast, which had higher than expected values for
Average and Variation Taxonomic distinctness measures, which as important
areas where sponges should be monitored to make sure the high levels of
biodiversity are protected. Taxonomic distinctness measures are useful for
initially assessing how the biodiversity is distributed, especially when using a
data set with uneven sampling effort, as it is robust to spatial and temporal bias
in the majority of cases. However, there was an outlier to the genera data
correlating well with the variation in species data in the case of a site
dominated by Haliclona sp (Lyttelton Harbour). In chapters three and four the
spatial and temporal variability of sponge assemblages of the Wellington South
Coast were explored creating both a species list for the area and an
understanding of how the sponge assemblage varies over time and space. There
were significant differences in the sponges assemblages in similar habitat types
over a scale of a few hundred metres. In addition, although all the sponge
assemblages changed seasonally, the changes at each sampling site responded
in a slightly different way most likely due to spatiotemporal variation in
environmental conditions. A similar seasonal pattern was also observed in
chapter five for sponge assemblages at Skomer Marine Reserve and this pattern
was also clear when using morphological monitoring methods. This means that
once a site has been mapped for biodiversity it is possible for some habitats to
use morphological monitoring to identify if the sponge assemblage is changing significantly saving time and money. The results from Indonesia (chapter six)
showed that although the sponge assemblages were changing significantly in
the actual species present and their abundances, the proportion of diversity
within each spatial level (quadrat, site and region) remained consistent when
sampled at the same time each year throughout the five year study. In species
rich assemblages there are a variety of life strategies that can respond
differently to shifts in environmental conditions and contribute to ecological
functioning in various ways. Various monitoring methods have been tested
using sponge assemblages over various spatial and temporal scales in this
thesis. Spatial, temporal and the interaction of spatial and temporal factors
were all important for identifying significant assemblage differences at all of the
sites. Further studies integrating the interaction of spatial and temporal factors
into understanding monitoring data sets are vital to understand the patterns of
assemblage variability and therefore incorporate into habitat management
plans.