高浓度环境颗粒和柴油机排气对褐挪威大鼠变应性气道疾病的影响。

Jack R Harkema, James G Wagner, Norbert E Kaminski, Masako Morishita, Gerald J Keeler, Jacob D McDonald, Edward G Barrett
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引用次数: 0

摘要

空气中细颗粒物(PM2.5)浓度增加;空气动力学直径<或= 2.5微米的颗粒物与哮喘患者急诊室就诊和住院的增加有关。来自当地固定燃烧源(如燃煤电厂)或移动机动车辆(如柴油动力卡车)的排放已被确定为过敏性气道疾病发展或恶化的潜在因素。本研究采用啮齿动物变应性气道疾病模型,研究了高浓度环境颗粒(CAPs)或柴油机排气(DEE)对致敏过敏原卵清蛋白(OVA)大鼠变应性气道疾病发展的影响。我们项目的总体目标是了解PM2.5对ova诱导的变应性气道疾病发展的影响。我们的具体目的是验证以下假设:(1)在OVA攻击期间暴露于cap会增强先前对过敏原敏感的大鼠的气道上皮重塑和炎症;(2)在OVA致敏或OVA攻击期间暴露于DEE会加剧大鼠气道上皮重塑和炎症。在DEE研究中,褐挪威(BN)大鼠每天鼻内(In)灌注0.5%卵细胞致敏,两周后连续3天给予In卵细胞或生理盐水刺激。在致敏或激发期间,大鼠暴露于稀释至30或300微克/立方米柴油废气颗粒(DEPs)质量浓度的DEE或过滤空气中。对于CAPs研究,使用了相同的OVA致敏和攻击大鼠模型,但暴露于密歇根州底特律市的CAPs仅限于OVA攻击期。两次单独的3天cap暴露(第1周,高平均质量浓度= 595微克/立方米;第2周,低平均质量浓度= 356微克/立方米)。在DEE和CAPs研究中,大鼠在最后一次OVA攻击后24小时被杀死,收集支气管肺泡灌洗液(BALF)并分析细胞和分泌介质,并对肺和鼻子进行组织病理学检查和上皮内粘膜物质(IM)的形态计量学分析。我们在底特律西南(SW)社区(一个环境PM2.5浓度升高的地区)进行的动物吸入研究结果表明,在过敏原挑战期间,暴露于主要与燃烧源排放相关的cap显着增强了ova诱导的过敏性气道疾病,其特征是肺嗜酸性粒细胞和淋巴细胞炎症浸润增加,导气管IM增加。以及黏液特异性蛋白和炎症细胞因子的BALF浓度升高。这些发现表明,来自固定燃烧源(如炼油厂、燃煤电厂、废物处理厂)的城市空气PM2.5可能会增加人类过敏性气道疾病(如儿童哮喘)的发展。先前在该社区进行的动物吸入研究也表明,这些细小的、环境燃烧产生的颗粒也可能加剧先前存在的过敏性气道疾病。与我们在底特律的CAPs研究相反,在过敏原致敏或刺激期间,对过敏原致敏的BN大鼠进行受控DEE暴露,只引起了过敏原诱发疾病特征的一些轻微改变。这一发现与其他报告的研究形成对比,这些研究表明,在某些啮齿动物模型中,相对较高暴露剂量的DEPs确实会增强过敏性气道疾病。这些研究之间差异的原因可能反映了暴露剂量、动物模型、暴露于过敏原和DEP的时间、过敏原致敏和激发方法的差异,或DEP之间的物理化学差异。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Effects of concentrated ambient particles and diesel engine exhaust on allergic airway disease in Brown Norway rats.

Increased concentrations of airborne fine particulate matter (PM2.5; particulate matter with an aerodynamic diameter < or = 2.5 microm) are associated with increases in emergency room visits and hospitalizations of asthmatic patients. Emissions from local stationary combustion sources (e.g., coal-burning power plants) or mobile motor vehicles (e.g., diesel-powered trucks) have been identified as potential contributors to the development or exacerbation of allergic airway disease. In the present study, a rodent model of allergic airway disease was used to study the effects of concentrated ambient particles (CAPs) or diesel engine exhaust (DEE) on the development of allergic airway disease in rats sensitized to the allergen ovalbumin (OVA). The overall objective of our project was to understand the effects of PM2.5 on the development of OVA-induced allergic airway disease. Our specific aims were to test the following hypotheses: (1) exposure to CAPs during OVA challenge enhances epithelial remodeling of the airway and inflammation in rats previously sensitized to the allergen; and (2) exposure to DEE during OVA sensitization, or during OVA challenge, exacerbates epithelial remodeling of the airway and inflammation in rats. In the DEE studies, Brown Norway (BN) rats were sensitized with three daily intranasal (IN) instillations of 0.5% OVA, and then two weeks later were challenged with IN OVA or saline for 3 consecutive days. Rats were exposed to DEE diluted to mass concentrations of 30 or 300 microg/m3 diesel exhaust particles (DEPs) or to filtered air during either the sensitization or challenge periods. For the CAPs studies, the same OVA sensitization and challenge rat model was used but exposures to Detroit, Michigan, CAPs were limited to the OVA challenge period. Two separate 3-day CAPs exposures were conducted (week 1, high mean mass concentration = 595 microg/m3; week 2, low mean mass concentration = 356 microg/m3) during OVA challenge. In both the DEE and CAPs studies, rats were killed 24 hours after the last OVA challenge, bronchoalveolar lavage fluid (BALF) was collected and analyzed for cellularity and secreted mediators, and lungs and nose were processed for histopathologic examination and morphometric analysis of intraepithelial mucosubstances (IM). The results of our animal inhalation studies in the southwest (SW) Detroit community, an area with elevated ambient PM2.5 concentrations, suggested that, during allergen challenge, exposure to CAPs that were predominantly associated with emissions from combustion sources markedly enhanced the OVA-induced allergic airway disease, which was characterized by an increased infiltration in the lungs of eosinophilic and lymphocytic inflammation, increased IM in conducting airways, and increased concentrations in BALF of mucin-specific proteins and inflammatory cytokines. These findings suggest that urban airborne PM2.5 derived from stationary combustion sources (e.g., refineries, coal-burning power plants, waste-treatment plants) may enhance the development of human allergic airway diseases like childhood asthma. Previous animal inhalation studies in this community have also suggested that these fine, ambient combustion-derived particles may also exacerbate preexisting allergic airway disease. In contrast to our CAPs studies in Detroit, the controlled DEE exposures of allergen-sensitized BN rats, during either allergen sensitization or challenge periods, caused only a few mild modifications in the character of the allergen-induced disease. This finding contrasts with other reported studies that indicate that DEPs at relatively higher exposure doses do enhance allergic airway disease in some rodent models. The reasons for these disparities between studies likely reflect differences in exposure dose, animal models, the timing of exposures to the allergens and DEP exposures, the methods of allergen sensitization and challenge, or physicochemical differences among DEEs.

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