Id |
Subject |
Object |
Predicate |
Lexical cue |
T1 |
142-265 |
DRI_Background |
denotes |
ZnO nanoparticles (ZnO-NPs) are emerging contaminants that raise the concerns of potential risk in the aquatic environment. |
T2 |
266-371 |
DRI_Background |
denotes |
It has been estimated that the environmental ZnO-NPs concentration is 76 μg/l in the aquatic environment. |
T3 |
372-536 |
DRI_Outcome |
denotes |
Our aim was to determine the aquatic toxicity of ZnO-NPs with chronic exposure at environmentally relevant concentrations using the nematode Caenorhabditis elegans. |
T4 |
537-747 |
DRI_Background |
denotes |
Two simulated environmentally relevant mediums-moderately hard reconstituted water (EPA water) and simulated soil pore water (SSPW)-were used to represent surface water and pore water in sediment, respectively. |
T5 |
748-856 |
DRI_Outcome |
denotes |
The results showed that the ZnO-NPs in EPA water has a much smaller hydrodynamic diameter than that in SSPW. |
T6 |
857-1137 |
DRI_Background |
denotes |
Although the ionic release of Zn ions increased time-dependently in both mediums, the Zn ions concentrations in EPA water increased two-fold more than that in SSPW at 48 h and 72 h. The ZnO-NPs did not induce growth defects or decrease head thrashes in C. elegans in either media. |
T7 |
1138-1340 |
DRI_Background |
denotes |
However, chronic exposure to ZnO-NPs caused a significant reduction in C. elegans body bends in EPA water even with a relatively low concentration (0.05 μg/l); similar results were not observed in SSPW. |
T8 |
1341-1487 |
DRI_Approach |
denotes |
Moreover, at the same concentrations (50 and 500 μg/l), body bends in C. elegans were reduced more severely in ZnO-NPs than in ZnCl2 in EPA water. |
T9 |
1625-1872 |
DRI_Outcome |
denotes |
Our results provide evidences that chronic exposure to ZnO-NPs under environmentally relevant concentrations causes metabolic and locomotive toxicities implicating the potential ecotoxicity of ZnO-NPs at low concentrations in aquatic environments. |