In Vitro Toxicology Group, Swansea University Medical School, Swansea University, Singleton Park Campus, Swansea, Wales, SA2 8PP, UK.
Part Fibre Toxicol. 2024 May 17;21(1):25. doi: 10.1186/s12989-024-00584-8.
Exposure to indoor air pollutants (IAP) has increased recently, with people spending more time indoors (i.e. homes, offices, schools and transportation). Increased exposures of IAP on a healthy population are poorly understood, and those with allergic respiratory conditions even less so. The objective of this study, therefore, was to implement a well-characterised in vitro model of the human alveolar epithelial barrier (A549 + PMA differentiated THP-1 incubated with and without IL-13, IL-5 and IL-4) to determine the effects of a standardised indoor particulate (NIST 2583) on both a healthy lung model and one modelling a type-II (stimulated with IL-13, IL-5 and IL-4) inflammatory response (such as asthma).Using concentrations from the literature, and an environmentally appropriate exposure we investigated 232, 464 and 608ng/cm of NIST 2583 respectively. Membrane integrity (blue dextran), viability (trypan blue), genotoxicity (micronucleus (Mn) assay) and (pro-)/(anti-)inflammatory effects (IL-6, IL-8, IL-33, IL-10) were then assessed 24 h post exposure to both models. Models were exposed using a physiologically relevant aerosolisation method (VitroCell Cloud 12 exposure system).No changes in Mn frequency or membrane integrity in either model were noted when exposed to any of the tested concentrations of NIST 2583. A significant decrease (p < 0.05) in cell viability at the highest concentration was observed in the healthy model. Whilst cell viability in the "inflamed" model was decreased at the lower concentrations (significantly (p < 0.05) after 464ng/cm). A significant reduction (p < 0.05) in IL-10 and a significant increase in IL-33 was seen after 24 h exposure to NIST 2583 (464, 608ng/cm) in the "inflamed" model.Collectively, the results indicate the potential for IAP to cause the onset of a type II response as well as exacerbating pre-existing allergic conditions. Furthermore, the data imposes the importance of considering unhealthy individuals when investigating the potential health effects of IAP. It also highlights that even in a healthy population these particles have the potential to induce this type II response and initiate an immune response following exposure to IAP.
室内空气污染物(IAP)的暴露最近有所增加,人们在室内(即家庭、办公室、学校和交通工具)的时间也有所增加。人们对健康人群中 IAP 的暴露增加知之甚少,对患有过敏性呼吸道疾病的人群更是知之甚少。因此,本研究的目的是建立一个经过良好表征的人肺泡上皮屏障(A549+PMA 分化的 THP-1,用 IL-13、IL-5 和 IL-4 孵育,有无 IL-13、IL-5 和 IL-4)的体外模型,以确定标准化室内颗粒物(NIST 2583)对健康肺模型和模拟 II 型(用 IL-13、IL-5 和 IL-4 刺激)炎症反应(如哮喘)的影响。
使用文献中的浓度和环境适宜的暴露浓度,我们分别研究了 NIST 2583 的 232、464 和 608ng/cm。暴露 24 小时后,用膜完整性(蓝色葡聚糖)、活力(台盼蓝)、遗传毒性(微核(Mn)测定)和(前/后)炎症效应(IL-6、IL-8、IL-33、IL-10)评估这两种模型。模型采用生理相关的气溶胶化方法(VitroCell Cloud 12 暴露系统)进行暴露。
在暴露于任何测试浓度的 NIST 2583 时,两种模型的 Mn 频率或膜完整性均无变化。在健康模型中,最高浓度下细胞活力显著降低(p<0.05)。而在“炎症”模型中,较低浓度下细胞活力降低(在 464ng/cm 后显著(p<0.05)。暴露于 NIST 2583(464、608ng/cm)24 小时后,“炎症”模型中 IL-10 显著降低(p<0.05),IL-33 显著升高。
总之,研究结果表明室内空气污染物(IAP)可能导致 II 型反应的发生,并加重已有的过敏性疾病。此外,数据表明,在研究 IAP 对健康的潜在影响时,需要考虑不健康人群。这也突出表明,即使在健康人群中,这些颗粒也有可能引起这种 II 型反应,并在接触 IAP 后引发免疫反应。