通过巨噬细胞反应的研究,对泰国清迈雾霾事件期间排放的颗粒物的肺毒性进行体外评估

K. Maciaszek, S. Gillies, S. Kawichai, T. Prapamontol, Teetawat Santijitpakdee, Wissanupong Kliengchuay, Narut Sahanavin, W. Mueller, S. Vardoulakis, Pawitrabhorn Samutrtai, J. Cherrie, David M. Brown, Kraichat Tantrakarnapa, H. Johnston
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引用次数: 1

摘要

泰国清迈每年在旱季(12月至4月)经历严重的雾霾污染,主要是由于当地和区域生物质燃烧(例如农业用地)。雾霾的主要成分是空气中的颗粒物(PM)。在雾霾事件期间,生物质燃烧可能是PM排放的主要来源,而在其他时间,交通排放占主导地位。交通产生的PM的危害以前已经进行了广泛的研究,但关于生物质燃烧排放的PM的毒性存在不确定性。研究人员在J774.1巨噬细胞中体外比较了2020年清迈雾霾事件期间和之后收集的PM10样本的毒性,因为它们负责清除吸入颗粒。柴油尾气颗粒和超细炭黑通常被用作PM的替代品,因此被纳入基准颗粒。在3.9-125µg ml−1的浓度下,对暴露24 h后的细胞毒性进行评估。细胞因子的产生(肿瘤坏死因子α (TNF-α)、白细胞介素(IL)-6、IL-1β、巨噬细胞炎症蛋白(MIP-2))被评估,并用光镜和扫描电镜观察细胞形态。测定了各颗粒的水动力直径、zeta电位和内毒素含量以及PM样品的金属含量。所有颗粒均诱导浓度依赖性细胞活力降低,TNF-α和MIP-2的产生增加。只有PM样品刺激IL-6的产生,只有非雾霾PM引起IL-1β的产生。对任何颗粒均未检测到IL-10产量的变化。PM样品和DEP引起细胞内形成液泡。内毒素和金属的浓度在非雾霾PM中最高,这可能解释了为什么它会引起最大的炎症反应。由于非雾霾PM比雾霾PM毒性更大,我们的研究结果表明PM排放源可以影响其毒性效力,更具体地说,生物质燃烧排放的PM可能比交通排放的PM毒性更小。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
In vitro assessment of the pulmonary toxicity of particulate matter emitted during haze events in Chiang Mai, Thailand via investigation of macrophage responses
Chiang Mai (Thailand) experiences severe haze pollution in the dry season (December–April) each year mainly due to local and regional biomass burning (e.g. of agricultural land). A major component of the haze is airborne particulate matter (PM). During haze events, biomass burning is likely to be the dominant source of PM emissions, and at other times emissions from traffic dominate. The hazard of traffic derived PM has been extensively investigated previously but there are uncertainties regarding the toxicity of PM emitted from biomass burning. The toxicity of PM10 samples collected during and after haze events in Chiang Mai in 2020 was compared in vitro in J774.1 macrophages as they are responsible for the clearance of inhaled particles. Diesel exhaust particles and ultrafine carbon black were included as benchmark particles as they have been commonly used as a surrogate for PM. Cytotoxicity was evaluated 24 h post exposure at concentrations of 3.9–125 µg ml−1. Cytokine production (tumour necrosis factor alpha (TNF-α), interleukin (IL)-6, IL-1β, macrophage inflammatory protein (MIP-2)) was assessed and cell morphology visualised using light and scanning electron microscopy. The hydrodynamic diameter, zeta potential and endotoxin content of all particles was assessed as well as the metal content of PM samples. All particles induced a concentration dependent decrease in cell viability and increased TNF-α and MIP-2 production. Only PM samples stimulated IL-6 production and only non-haze PM caused IL-1β production. No change in IL-10 production was detected for any particle. PM samples and DEP caused vacuole formation in cells. The concentrations of endotoxin and metals were highest in non-haze PM, which may explain why it induced the greatest inflammatory response. As non-haze PM was more toxic than haze PM, our results indicate that the source of PM emissions can influence its toxic potency and more specifically, that PM emitted from biomass burning may be less toxic than PM emitted from traffic.
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