9 research outputs found

    Mixed messages from benthic microbial communities exposed to nanoparticulate and ionic silver: 3D structure picks up nano-specific effects, while EPS and traditional endpoints indicate a concentration-dependent impact of silver ions

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    Silver nanoparticles (AgNP) are currently defined as emerging pollutants in surface water ecosystems. Whether the toxic effects of AgNP towards freshwater organisms are fully explainable by the release of ionic silver (Ag+) has not been conclusively elucidated. Long-term effects to benthic microbial communities (periphyton) that provide essential functions in stream ecosystems are unknown. The effects of exposure of periphyton to 2 and 20 μg/L Ag+ (AgNO3) and AgNP (polyvinylpyrrolidone stabilised) were investigated in artificial indoor streams. The extracellular polymeric substances (EPS) and 3D biofilm structure, biomass, algae species, Ag concentrations in the water phase and bioassociated Ag were analysed. A strong decrease in total Ag was observed within 4 days. Bioassociated Ag was proportional to dissolved Ag indicating a rate limitation by diffusion across the diffusive boundary layer. Two micrograms per liter of AgNO3 or AgNP did not induce significant effects despite detectable bioassociation of Ag. The 20-μg/L AgNO3 affected green algae and diatom communities, biomass and the ratio of polysaccharides to proteins in EPS. The 20-μg/L AgNO3 and AgNP decreased biofilm volume to about 50 %, while the decrease of biomass was lower in 20 μg/L AgNP samples than the 20-μg/L AgNO3 indicating a compaction of the NP-exposed biofilms. Roughness coefficients were lower in 20 μg/L AgNP-treated samples. The more traditional endpoints (biomass and diversity) indicated silver ion concentration-dependent effects, while the newly introduced parameters (3D structure and EPS) indicated both silver ion concentration-dependent effects and effects related to the silver species applied

    Ecotoxicology of nanoparticles – effects on organisms from activated sludge in wastewater treatment plants

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    Among all nanomaterials, which are intentionally manufactured and applied, nanosilver (nAg) is one of the most frequently applied nanomaterials. It is introduced into wastewater treatment plants (WWTPs) due to its use as antimicrobial resource in household and medical care products and hence concern raised regarding its impact on activated sludge organisms and their purification efficiency. Within this thesis, the effects of nAg on single species, simple food chains and communities related to activated sludge were investigated. Among all tested species in this thesis, the gammaproteobacteria R. planticola was the most sensitive organism regarding the tested nAg material, NM-300K. The environmental risk assessment (ERA), based on an assumed predicted environmental concentration derived from modeled concentrations of other types of nAg, revealed no risk for the activated sludge. This result should be interpreted with care, considering the tolerantly chosen safety factor for calculation of the predicted no effect concentration and the assumptions which were made concerning environmental concentrations. Differences in acute toxic effects of nAg on the ciliate P. tetraurelia were observed depending on the type of medium and the exposure pathway (via medium or via bacterial food). More detailed investigations are required to analyze the distribution, availability and uptake of nAg into ciliates in the respective tests. In chronic experiments concentration response was very steep in the range between the effect concentration determined in acute toxicity testing (resulting in 100% mortality) and a tenfold lower concentration (no effect observed) for both exposure pathways. Community experiments with activated sludge exposed to realistic and high concentrations of nAg revealed acute effects on the protozoan community at high nAg concentration using multivariate statistics for data analysis. In contrast, the sludge biotic index was not meaningful for data interpretation, as no differences were observed between the samples of different treatments. For chronic testing, more preliminary work is required to develop a protocol for artificial wastewater which serves the needs of activated sludge organisms over longer time periods and which retains a typical composition of the activated sludge community

    Dynamic light-scattering measurement comparability of nanomaterial suspensions

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    Increased use of nanomaterials in everyday products leads to their environmental release and therefore, the information need on their fate and behaviour. Nanomaterials have to be suspended with high repeatability and comparability for studies on environmental effects. They also have to be well characterised with a focus on the state of agglomeration and particle size distribution. Dynamic lightscattering (DLS) is a common technique used for these measurements. If suspensions are prepared in different laboratories, then concern has risen about the comparability of the measured results, especially when different DLS instruments are used. Therefore, for quality assurance, a round-robin test was conducted to assess the comparability of different DLS instruments and a dispersion protocol in ten independent laboratories. Polystyrene and TiO2 were chosen as test (nano)materials. For the comparability of the DLS instruments, the average sizes of the PSL and a stabilised TiO2 suspension were measured. The measured average hydrodynamic diameter shows an overall good inter-laboratory comparability. For the PSL suspension, an average hydrodynamic diameter of 201 ± 13 nm and for the TiO2 suspension an average diameter of 224 ± 24 nm were detected. For the TiO2 suspension that was prepared at each laboratory following an established suspension preparation protocol, an average hydrodynamic diameter of 211 ± 11 nm was detected. The measured average particle size (mode) increased up to 284 nm with a high standard deviation of 119 nm if the preparation protocol could not established and different procedures or different equipment were employed. This study shows that no significant differences between the employed DLS instrument types were determined. It was also shown that comparable measurements and suspension preparation could be achieved if welldefined suspension preparation protocols and comparable equipment can be used
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