TY - JOUR
T1 - Risk assessment of salinity and turbidity in Victoria (Australia) to stream insects' community structure does not always protect functional traits
AU - Kefford, Ben
AU - Schäfer, R
AU - Metzeling, Leon
PY - 2012
Y1 - 2012
N2 - Ecological risk assessments mostly consider measures of community composition (structure) across large spatial scales. These assessments, using species sensitivity distributions (SSDs) or the relative species retention (RSR), may not be protective of ecosystem functions and services at smaller spatial scales. Here we examine how changes in biological traits, as proxy for ecosystem functions/services, at a fine spatial scale relate to larger scale assessment of structure. We use functional traits of stream insect species in south-east Australia in two habitats (riffle and edge/pool). We find that the protection of community structure in terms of 95% of species over multiple sites against adverse effects of salinity (as electrical conductivity) and turbidity will mostly, but not always, protect traits at smaller scales. Considering different combinations of trait modalities, contaminants and habitat, a mean of 17.5% (range 0%–36.8) of cases would result in under-protection of trait modalities despite protecting species composition (in terms of Jaccard's Index). This under-protection of trait modalities is only because of the different spatial scales that community structure and the traitswere considered. We recommend that where the protection of biological traits, ecosystem functions or ecosystem services from tressors is a management goal, protective targets should not be solely set using measures of community structure such as SSDs or RSR. To protect both structural and functional attributes separate risk assessments should be done.
AB - Ecological risk assessments mostly consider measures of community composition (structure) across large spatial scales. These assessments, using species sensitivity distributions (SSDs) or the relative species retention (RSR), may not be protective of ecosystem functions and services at smaller spatial scales. Here we examine how changes in biological traits, as proxy for ecosystem functions/services, at a fine spatial scale relate to larger scale assessment of structure. We use functional traits of stream insect species in south-east Australia in two habitats (riffle and edge/pool). We find that the protection of community structure in terms of 95% of species over multiple sites against adverse effects of salinity (as electrical conductivity) and turbidity will mostly, but not always, protect traits at smaller scales. Considering different combinations of trait modalities, contaminants and habitat, a mean of 17.5% (range 0%–36.8) of cases would result in under-protection of trait modalities despite protecting species composition (in terms of Jaccard's Index). This under-protection of trait modalities is only because of the different spatial scales that community structure and the traitswere considered. We recommend that where the protection of biological traits, ecosystem functions or ecosystem services from tressors is a management goal, protective targets should not be solely set using measures of community structure such as SSDs or RSR. To protect both structural and functional attributes separate risk assessments should be done.
KW - Biological traits
KW - Stream macroinvertebrates
KW - Salinization
KW - Suspended sediments
KW - Spatial scale.
U2 - 10.1016/j.scitotenv.2011.05.056
DO - 10.1016/j.scitotenv.2011.05.056
M3 - Article
SN - 0048-9697
VL - 415
SP - 61
EP - 68
JO - Science of the Total Environment
JF - Science of the Total Environment
ER -