HCTm CO., LTD, Seoicheon-ro 578 beon-gil, Majang-myeon, Icheon, 17383, Korea.
Department of Mechanical Engineering, Hanyang University, Ansan, Korea.
Arch Toxicol. 2020 Mar;94(3):773-784. doi: 10.1007/s00204-020-02660-2. Epub 2020 Mar 10.
Recently revised OECD inhalation toxicity testing guidelines require measurements of lung burden immediately after and for periods following exposure for nanomaterials. Lung burden is a function of pulmonary deposition and retention of nanoparticles. Using lung burden studies as per OECD guidelines, it may be possible to assess clearance mechanisms of nanoparticles. In this study, male rats were exposed to silver nanoparticle (AgNP) aerosols (18.1-19.6 nm) generated from a spark generator. Exposure groups consisted of (1) control (fresh air), (2) low (31.2 ± 8.5 µg/m), (3) moderate (81.8 ± 11.4 µg/m), and (4) high concentrations (115.6 ± 30.5 µg/m). Rats were exposed for 6-h/day, 5-days/week for 4 weeks (28-days) based on the revised OECD test guideline 412. Bronchoalveolar lavage (BAL) fluids were collected on post-exposure observation (PEO)-1 and PEO-7 days and analyzed for inflammatory cells and inflammatory biomarkers. The lung burdens of Ag from AgNPs were measured on PEO-1, PEO-7, and PEO-28 days to obtain quantitative mass concentrations per lung. Differential counting of blood cells and inflammatory biomarkers in BAL fluid and histopathological evaluation of lung tissue indicated that exposure to the high concentrations of AgNP aerosol induced inflammation at PEO-1, slowly resolved at PEO-7 and completely resolved at PEO-28 days. Lung burden measurement suggested that Ag from AgNPs was cleared through two different modes; fast and slow clearance. The fast clearance component was concentration-dependent with half-times ranging from two to four days and clearance rates of 0.35-0.17/day from low to high concentrations. The slow clearance had half-times of 100, 57, and 76 days and clearance rates of 0.009, 0.012, and 0.007/day for the high, moderate and low concentration exposure. The exact mechanism of clearance is not known currently. The fast clearance component which was concentration-dependent could be dependent on the dissolution of AgNPs and the slow clearance would be due to slow clearance of the low dissolution AgNPs secondary particles originating from silver ions reacting with biogenic anions. These secondary AgNPs might be cleared by mechanisms other than dissolution such as mucociliary escalation, translocation to the lymphatic system or other organs.
最近修订的经合组织吸入毒性测试指南要求在暴露后立即和暴露后一段时间内测量肺负荷,以用于纳米材料。肺负荷是纳米颗粒肺部沉积和保留的函数。根据经合组织指南使用肺负荷研究,有可能评估纳米颗粒的清除机制。在这项研究中,雄性大鼠暴露于银纳米颗粒(AgNP)气溶胶(18.1-19.6nm),气溶胶由火花发生器产生。暴露组包括(1)对照组(新鲜空气)、(2)低浓度组(31.2±8.5μg/m)、(3)中浓度组(81.8±11.4μg/m)和(4)高浓度组(115.6±30.5μg/m)。大鼠每天暴露 6 小时,每周暴露 5 天,共 4 周(28 天),依据修订后的经合组织测试指南 412。在暴露后观察 1 天(PEO-1)和暴露后观察 7 天(PEO-7)时收集支气管肺泡灌洗液(BAL),并分析炎症细胞和炎症生物标志物。在 PEO-1、PEO-7 和 PEO-28 天测量 AgNP 中 Ag 的肺负荷,以获得每肺定量质量浓度。BAL 液中血液细胞和炎症生物标志物的差异计数以及肺组织的组织病理学评估表明,高浓度 AgNP 气溶胶暴露在 PEO-1 时引起炎症,在 PEO-7 时缓慢缓解,在 PEO-28 天完全缓解。肺负荷测量表明,AgNP 中的 Ag 通过两种不同的模式清除;快速清除和缓慢清除。快速清除组分与浓度相关,半衰期范围为 2 至 4 天,清除率为 0.35-0.17/天,从低浓度到高浓度。缓慢清除的半衰期分别为 100、57 和 76 天,清除率分别为 0.009、0.012 和 0.007/天,用于高、中、低浓度暴露。目前尚不清楚确切的清除机制。与浓度相关的快速清除组分可能依赖于 AgNP 的溶解,而缓慢清除则是由于源自银离子与生物阴离子反应的低溶解 AgNP 次生颗粒的缓慢清除所致。这些次生 AgNP 可能通过与溶解不同的机制被清除,例如黏液纤毛上升、转移到淋巴系统或其他器官。