CBET Research group, Dept. of Zoology and Animal Cell Biology, Research Centre for Experimental Marine Biology and Biotechnology PiE and Science and Technology Faculty, University of the Basque Country (UPV/EHU), Sarriena z/g, E-48940 Leioa, Basque Country, Spain.
European Commission, JRC Directorate F - Health, Consumers and Reference Materials, Via E. Fermi, 2749, I-21027 Ispra, VA, Italy.
Sci Total Environ. 2018 Nov 15;642:1209-1220. doi: 10.1016/j.scitotenv.2018.06.128. Epub 2018 Jun 20.
Effects of silver nanoparticles (Ag NPs) on freshwater species have been reported in several studies, but there is not information on the potential long-term consequences of a previous exposure. In this work, we investigated the long-term effects of maltose-coated Ag NPs (20 nm) and of ionic silver (10 μg/L) after 21 days of exposure and at 6 months post-exposure (mpe) in adult zebrafish. Exposure resulted in significant silver accumulation in the whole body of fish exposed to ionic silver, but not in those exposed to Ag NPs. However, autometallography revealed metal accumulation in the liver and intestine of fish treated with the two silver forms and especially in the intestine of fish exposed to Ag NPs. X-ray microanalysis showed the presence of silver in gills, liver and intestine and of Ag NPs in gill and liver cells. Inflammation and hyperplasia were evident in the gills after both treatments and these histopathological conditions remained at 6 mpe. According to the hepatic transcriptome analysis, at 3 days ionic silver regulated a larger number of transcripts (410) than Ag NPs (129), while at 21 days Ag NPs provoked a stronger effect (799 vs 165 regulated sequences). Gene ontology terms such as "metabolic processes" and "response to stimulus" appeared enriched after all treatments, while "immune system" or "reproductive processes" were specifically enriched after the exposure to Ag NPs. This suggests that the toxicity of Ag NPs may not be solely related to the release of Ag ions, but also to the NP form. No evident effects were found on protein oxidation or on hepatocyte lysosomal membrane stability during exposure, but effects recorded on liver lysosomes and persistent damage on gill tissue at 6 mpe could indicate potential for long-term effects in exposed fish.
已有多项研究报道了纳米银(Ag NPs)对淡水物种的影响,但关于先前暴露的潜在长期后果的信息尚不清楚。在这项工作中,我们研究了麦芽糖包覆的 Ag NPs(20nm)和离子银(10μg/L)在暴露 21 天后和暴露后 6 个月(mpe)对成年斑马鱼的长期影响。暴露导致暴露于离子银的鱼体全身的银积累显著,但暴露于 Ag NPs 的鱼体则没有。然而,自动金属成像显示,两种银形式处理的鱼的肝脏和肠道中存在金属积累,尤其是暴露于 Ag NPs 的鱼的肠道中。X 射线微分析显示银存在于鳃、肝脏和肠道中,Ag NPs 存在于鳃和肝细胞中。两种处理后鱼的鳃均出现炎症和增生,这些组织病理学状况在 6 mpe 时仍然存在。根据肝转录组分析,离子银在 3 天时调节的转录本数量(410 个)多于 Ag NPs(129 个),而在 21 天时 Ag NPs 引起的影响更强(799 个 vs 165 个调节序列)。GO 术语如“代谢过程”和“对刺激的反应”在所有处理后均出现富集,而“免疫系统”或“生殖过程”则在暴露于 Ag NPs 后特异性富集。这表明 Ag NPs 的毒性可能不仅仅与 Ag 离子的释放有关,还与 NP 形式有关。在暴露期间,没有发现对蛋白质氧化或肝细胞溶酶体膜稳定性的明显影响,但在 6 mpe 时记录到的对肝溶酶体的影响和对鳃组织的持续损伤可能表明暴露鱼存在长期影响的潜在风险。