Lacave José María, Fanjul Álvaro, Bilbao Eider, Gutierrez Nerea, Barrio Irantzu, Arostegui Inmaculada, Cajaraville Miren P, Orbea Amaia
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.
Dept. of Applied Mathematics, Statistics and Operations Research, Science and Technology Faculty, and Basque Center for Applied Mathematics - BCAM, University of the Basque Country (UPV/EHU), Leioa, Spain.
Comp Biochem Physiol C Toxicol Pharmacol. 2017 Sep;199:69-80. doi: 10.1016/j.cbpc.2017.03.008. Epub 2017 Mar 18.
The extensive use and release to the aquatic environment of silver nanoparticles (NPs) could lead to their incorporation into the food web. Brine shrimp larvae of 24h showed low sensitivity to the exposure to PVP/PEI-coated Ag NPs (5nm), with EC values at 24h of 19.63mgAgL, but they significantly accumulated silver after 24h of exposure to 100μgL of Ag NPs. Thus, to assess bioaccumulation and effects of silver transferred by the diet in zebrafish, brine shrimp larvae were exposed to 100ngL of Ag NPs as an environmentally relevant concentration or to 100μgL as a potentially effective concentration and used to feed zebrafish for 21days. Autometallography revealed a dose- and time-dependent metal accumulation in the intestine and in the liver of zebrafish. Three-day feeding with brine shrimps exposed to 100ngL of Ag NPs was enough to impair fish health as reflected by the significant reduction of lysosomal membrane stability and the presence of vacuolization and necrosis in the liver. However, dietary exposure to 100μgL of Ag NPs for 3days did not significantly alter gene transcription levels, neither in the liver nor in the intestine. After 21days, biological processes such as lipid transport and localization, cellular response to chemical stimulus and response to xenobiotic stimulus were significantly altered in the liver. Overall, these results indicate an effective dietary transfer of silver and point out to liver as the main target organ for Ag NP toxicity in zebrafish after dietary exposure.
银纳米颗粒(NPs)在水环境中的广泛使用和排放可能导致它们进入食物网。24小时大的卤虫幼体对暴露于PVP/PEI包覆的5纳米银纳米颗粒的敏感性较低,24小时的EC值为19.63mgAg/L,但在暴露于100μg/L的银纳米颗粒24小时后,它们显著积累了银。因此,为了评估斑马鱼通过饮食摄入银的生物累积和影响,卤虫幼体暴露于100ng/L的银纳米颗粒(作为环境相关浓度)或100μg/L(作为潜在有效浓度),并用于喂养斑马鱼21天。自动金相分析显示,斑马鱼的肠道和肝脏中金属积累呈剂量和时间依赖性。用暴露于100ng/L银纳米颗粒的卤虫喂养三天就足以损害鱼类健康,这表现为溶酶体膜稳定性显著降低以及肝脏中出现空泡化和坏死。然而,饮食中暴露于100μg/L的银纳米颗粒三天,无论是在肝脏还是在肠道中,都没有显著改变基因转录水平。21天后,肝脏中脂质运输和定位、细胞对化学刺激的反应以及对外源生物刺激的反应等生物学过程发生了显著改变。总体而言,这些结果表明银通过饮食有效转移,并指出肝脏是斑马鱼在饮食暴露后银纳米颗粒毒性的主要靶器官。