[
Sci Total Environ,
2020]
Five conazole fungicides (CFs) (epoxiconazole, tebuconazole, myclobutanil, uniconazole (P), rac-uniconazole, and diniconazole) were tested in order to provide additional information on i) the effects of CFs on the nematode Caenorhabditis elegans and on the aquatic insect Chironomus riparius under acute exposure scenarios and in multi-generation exposure studies, taking advantage of the short life cycle of nematodes and ii) on the bioaccumulation (earthworm Eisenia andrei) profiles of CFs including also the enantiomer-specific assessment of degradation in soils and uptake/elimination by earthworms. Acute toxicity was considered low following the exposure of up to 2.5mg of CFs per liter of the test medium. In a multigeneration study on nematodes, all five generations exposed to epoxiconazole were significantly negatively affected in terms of reproductive efficiency, and the severity of effects increased from F0 to F1 generation and was sustained thereafter. Adverse effects were also observed in the case of uniconazole (P) and diniconazole, and similarly to epoxiconazole, the effects occurred within the active life of the pesticides and were assumed to be based on their half-lives in soil (e.g., 53.3 to 691days for uniconazole and diniconazole in our study) and in sediment/water. Bioaccumulation of diniconazole and uniconazole by earthworms varied between soils (Lufa 2.1Lufa 2.4>sandy soil > Lufa 2.2) and compounds (diniconazole > uniconazole) and was enantioselective. Earthworms preferentially accumulated R-uniconazole as a result of faster elimination of the S-form, which was evidenced from the enantiomer-specific uptake/elimination rate constants derived from the bioaccumulation profiles. Our results suggest that multigeneration exposure studies can advantageously be used for assessing the long-term and trans-general effects of pesticides. Also, the enantioselectivity in bioaccumulation observed for both uniconazole and diniconazole suggests that enantioselectivity in the fate and effects should be considered when exploring ways for safer and sustainable use of chiral pesticides.
[
Environ Int,
2020]
Vehicles generate particulate matter (PM) in significant amounts as their brake systems wear. These particles can influence air quality and their transport/deposition may affect the edaphic and aquatic ecosystems. As part of the LOWBRASYS H2020 project, new more eco-friendly brake disc and pad formulations were developed. PMs generated from traditional (FM1-BD1) and innovative (FM4-BD2, FMB-BD7) brake systems in bench tests were studied. The PMs' physical/chemical characteristics were preliminarily investigated. To study the possible environmental impact of the nano-micro particulate, we used a battery of ecotoxicological tests. We employed the microalga Pseudokirchneriella subcapitata, the crustacean Daphnia magna and the bacteria Vibrio fischeri as aquatic bioindicators, while for the edaphic ecosystem we used the seeds of Lepidium sativum and Sorghum saccharatum, the nematode Caenorhabditis elegans, the earthworm Eisenia andrei and the ameba Dictyostelium discoideum. The results showed a higher sensitivity of the freshwater organisms exposed to the soluble PM fraction, with respect to the edaphic ones. FM4-BD2 brake formulation was slightly more toxic for algae (200mg/L) than FM1-BD1 (500mg/L). The new system FMB-BD7 particulate was not harmful for crustacean survival, and resulted weakly toxic for algal reproduction only at 500mg/L. The particulate material per se was found to affect the algal reproduction. No toxic effects were found on nematodes, earthworms and seeds up to 1000mg/L. However, in D. discoideum the reproduction rate was significantly reduced starting from 100mg/L; and the lysosomal membrane stability showed a relevant alteration also at minimal concentration (0.1mg/L). The results demonstrated a minimal risk for biodiversity of the particulates from the different brake systems and highlighted a more eco-friendly performance the new brake-pad FMB-BD7. However, the occurrence of sublethal effects should be considered as a possible contribution of the particle toxicity to the biological effects of the environmental pollution.