1 Department of Freshwater Ecology, National Environmental Research Institute, Aarhus University, Aarhus University2 Department of Bioscience - Stream and Wetland Ecology, Department of Bioscience, Science and Technology, Aarhus University3 Department of Bioscience - Catchment Science and Environmental Management, Department of Bioscience, Science and Technology, Aarhus University4 Department of Bioscience - Stream and Wetland Ecology, Department of Bioscience, Science and Technology, Aarhus University5 Department of Bioscience - Catchment Science and Environmental Management, Department of Bioscience, Science and Technology, Aarhus University
Stream ecosystems are impacted by numerous anthropogenic stressors, and they remain some of the most impaired ecosystems on earth in terms of species extinction rates. This emphasises the importance of a yet unresolved question – whether these ecosystems are able to maintain their ecological functions. In consequence, it is highly important to address and characterise relations between stream functions and anthropogenic stress. In streams, fungi and bacteria are key organism groups in the decomposition and conversion of riparian plant litter into more palatable food resources for macroinvertebrate shredders and collectors (Bärlocher, 2005). We measured mass loss in beech leaves (Fagus sylvatica) using net bags with mesh size < 500 μm in 14 Danish streams draining catchments that represented a gradient in agricultural activity. In each stream 30 leaf bags were mounted to the stream bed of which half were positioned at sites characterised by low flow and fine particulate substratum and the other half at sites characterised by turbulent flow and coarse substratum. Leaves were submerged in the streams from April to July. Concurrently, water samples were collected during storm flow events using event triggered samplers and analysed for 18 pesticide compounds. Leaf breakdown coefficients (k) were reduced by a factor 3-8 in streams where fungicides were detected compared to streams where fungicides were not detected. Breakdown coefficients were, furthermore, significantly lower (P<0.05) for leaf packs that were positioned at sites with low flow compared to sites with turbulent flow. Moreover, we calculated summed Toxic Units (TU) for all pesticides in each sample by weighing the toxic contribution of each compound against its toxicity for Selenastrum capricornotum (a microbial standard test organism). Of all measured environmental parameters (physical and chemical stream properties, and catchment properties) the TUS.capricornotum was the parameter most strongly correlated to breakdown coefficients (r=0.69, P<0.001). Our study is the first to evaluate effects of pesticides on microbial litter degradation in the field. The results clearly emphasise the importance of considering microbial litter breakdown as endpoint when evaluating the effects of anthropogenic stressors in streams. Agricultural pesticides could have the potential to alter the entire flux of energy through ecosystems – an effect that is further enhanced when physical conditions in streams are poor. In addition, our study shows that TUS.capricornotum is applicable for predicting effects of agricultural pesticides on microbial communities.
Main Research Area:
science for the environment - environment for science, 2011