Abstract
The application of engineered silver nanoparticles (AgNPs) in a considerable amount of registered commercial products inevitably will result in the continuous release of AgNPs into the natural aquatic environment. Therefore, native biofilms, as the prominent life form of microorganisms in almost all known ecosystems, will be subjected to AgNP exposure. Despite the exponentially growing research activities worldwide, it is still difficult to assess nanoparticle-mediated toxicity in natural environments. In order to obtain an ecotoxicologically relevant exposure scenario, we performed experiments with artificial stream mesocosm systems approaching low dose AgNP concentrations close to predicted environmental concentrations. Pregrown freshwater biofilms were exposed for 14 days to citrate-stabilized AgNPs at a concentration of 600 μg l-1 in two commonly used sizes (30 and 70 nm). Sublethal effects of AgNP treatment were assessed with regard to biofilm structure by gravimetric measurements (biofilm thickness and density) and by two biomass parameters, chlorophyll a and protein content. The composition of bacterial biofilm communities was characterized by t-RFLP fingerprinting combined with phylogenetic studies based on the 16S gene. After 14 days of treatment, the structural parameters of the biofilm such as thickness, density, and chlorophyll a and protein content were not statistically significantly changed by AgNP exposure. Furthermore, t-RFLP fingerprint analysis showed that the bacterial diversity was not diminished by AgNPs, as calculated by Shannon Wiener and evenness indices. Nevertheless, t-RFLP analysis also indicated that AgNPs led to an altered biofilm community composition as was shown by cluster analysis and multidimensional scaling (MDS) based on the Bray Curtis index. Sequence analysis of cloned 16S rRNA genes further revealed that changes in community composition were related with the displacement of putatively AgNP-sensitive bacterial taxa Actinobacteria, Chloroflexi, and Cyanobacteria by taxa known for their enhanced adaptability towards metal stress, such as Acidobacteria, Sphingomonadales, and Comamonadaceae. This measurable community shift, even after low dose AgNP treatment, causes serious concerns with respect to the broad application of AgNPs and their potentially adverse impact on the ecological function of lotic biofilms, such as biodegradation or biostabilization.
Highlights
During the last decade, engineered silver nanoparticles (AgNPs) have become a substantial part of modern commodities, with applications in textiles, personal care products and pharmaceuticals
Stable water parameters allowed for interpretation of the data obtained from the analysis of the Effects of silver nanoparticle treatment on the structure and community composition of freshwater biofilms structure and bacterial community composition of the lotic biofilms as a consequence of applied application of engineered silver nanoparticles (AgNPs)
We proofed a bacterial community composition which reflects the bacterial community composition commonly found in stream biofilm communities [54]
Summary
During the last decade, engineered silver nanoparticles (AgNPs) have become a substantial part of modern commodities, with applications in textiles, personal care products and pharmaceuticals. The aggregation of AgNPs can result in their sedimentation accompanied by accumulation in microbial biofilms [8], which serve as a sink for organic and inorganic pollutants. Due to their metabolic and genetic diversity, bacterial biofilm communities play a key role in the production and degradation of NOM; cycling of nitrogen, phosphorous, sulfur and metals [9]; and transformation and/ or degradation of pollutants. An enrichment of AgNPs or their transformation products in freshwater biofilms by contamination or redistribution may lead to comparable toxic effects. Because bactericidal properties of AgNPs are attributed to the release of Ag+-ions by oxidative dissolution [11,12,13], AgNPs might serve as a continuous source for Ag+-ions and have a long-term impact on biofilms
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