Hallberg Lance M, Ward Jonathan B, Hernandez Caterina, Ameredes Bill T, Wickliffe Jeffrey K
Res Rep Health Eff Inst. 2015 Jan(184):87-105; discussion 141-71.
In 2001, the U.S. Environmental Protection Agency (EPA*) and the California Air Resources Board (CARB) adopted new standards for diesel fuel and emissions from heavy-duty diesel engines. By 2007, diesel engines were required to meet these new standards for particulate matter (PM), with other standards to follow. Through a combination of advanced compression-ignition engine technology, development of exhaust aftertreatment systems, and reformulated fuels, stringent standards were introduced. Before the 2007 standards were put in place by the EPA, human health effects linked to diesel exhaust (DE) exposure had been associated with diesel-fuel solvent and combustion components. In earlier research, diesel engine exhaust components were, in turn, linked to increased mutagenicity in cultures of Salmonella typhimurium and mammalian cells (Tokiwa and Ohnishi 1986). In addition, DE was shown to increase both the incidence of tumors and the induction of 8-hydroxy-deoxyguanosine (8-OHdG) adducts in rodents (Ichinose et al. 1997) and total DNA adducts in rats (Bond et al. 1990). Furthermore, DE is composed of a complex mixture of polycyclic aromatic hydrocarbons (PAHs) and particulates. One such PAH, 3-nitrobenzanthrone (3-NBA), is also found in urban air. 3-NBA has been observed to induce micronucleus formation in the DNA of human hepatoma cells (Lamy et al. 2004). The current study is part of the Advanced Collaborative Emissions Study (ACES), a multidisciplinary program carried out by the Health Effects Institute and the Coordinating Research Council. Its purpose was to determine whether recent improvements in the engineering of heavy-duty diesel engines reduce the toxicity associated with exposure to DE components. To this end, we evaluated potential genotoxicity and induction of oxidative stress in bioassays of serum and tissues from Wistar Han rats chronically exposed--for up to 24 months--to DE from a 2007-compliant diesel engine (new-technology diesel exhaust, or NTDE). Genotoxicity was measured as DNA strand breaks in lung tissue, using an alkaline-modified comet assay. As a correlate of possible DNA damage evaluated in the comet assay, concentrations of the free DNA adduct 8-OHdG were evaluated in serum by a competitive enzyme-linked immunosorbent assay (ELISA). The 8-OHdG fragment found in the serum is a specific biomarker for the repair of oxidative DNA damage. In addition, an assay for thiobarbituric acid reactive substances (TBARS) was used to assess oxidative stress and damage in the form of lipid peroxidation in the hippocampus region of the brains of the DE-exposed animals. These endpoints were evaluated at 1, 3, 12, and 24 months of exposure to DE or to a control atmosphere (filtered air). At the concentrations of DE evaluated, there were no significant effects of exposure in male or female rats after 1, 3, 12, or 24 months in any measure of DNA damage in the comet assay (%DNA in tail, tail length, tail moment, or olive moment). The comparison of exposure groups versus control and the comparison of groups by sex for 1 and 3 months of exposure showed no significant differences in serum 8-OHdG concentrations (P > 0.05). The concentrations of 8-OHdG in all exposure groups at 3 months were higher than those in exposure groups at any other time point (P < 0.05). Looking at the levels of 8-OHdG in serum in the 12-month and 24-month groups, we saw a significant difference from control in the 12-month group at the mid and high levels (P < 0.05), as well as some other scattered changes. Sex differences were noted in the 12-month high-level group (P < 0.05). However, these differences did not follow an exposure-dependent pattern. All other comparisons were not significant (P > 0.05). Hippocampal concentrations of TBARs, measured as malondialdehyde (MDA), showed some small and scattered changes in groups exposed to different levels of DE and at different time points, but we did not consider these to be exposure-related. We concluded that exposure to DE in these rats did not produce any significant increase in oxidative damage to lipids or damage to DNA in the form of strand breaks.
2001年,美国环境保护局(EPA*)和加利福尼亚空气资源委员会(CARB)采用了柴油燃料及重型柴油发动机排放的新标准。到2007年,柴油发动机被要求符合颗粒物(PM)的这些新标准,其他标准随后出台。通过先进的压缩点火发动机技术、废气后处理系统的开发以及重新配方的燃料相结合,引入了严格的标准。在EPA实施2007年标准之前,与接触柴油废气(DE)相关的人体健康影响一直与柴油燃料溶剂和燃烧成分有关。在早期研究中,柴油发动机废气成分又与鼠伤寒沙门氏菌和哺乳动物细胞培养物中致突变性增加有关(常盘和大西,1986年)。此外,DE被证明会增加啮齿动物肿瘤的发生率以及8-羟基脱氧鸟苷(8-OHdG)加合物的诱导(市野等,1997年)和大鼠总DNA加合物(邦德等,1990年)。此外,DE由多环芳烃(PAHs)和颗粒物的复杂混合物组成。一种这样的PAH,3-硝基苯并蒽酮(3-NBA),也存在于城市空气中。已观察到3-NBA会诱导人肝癌细胞DNA中的微核形成(拉米等,2004年)。当前的研究是高级协作排放研究(ACES)的一部分,ACES是由健康影响研究所和协调研究委员会开展的一个多学科项目。其目的是确定重型柴油发动机工程方面最近的改进是否会降低与接触DE成分相关的毒性。为此,我们评估了长期(长达24个月)接触符合2007年标准的柴油发动机的DE(新技术柴油废气,或NTDE)的Wistar Han大鼠血清和组织生物测定中的潜在遗传毒性和氧化应激诱导情况。使用碱性改良彗星试验测量肺组织中的DNA链断裂来评估遗传毒性。作为彗星试验中评估的可能DNA损伤的一个相关指标,通过竞争性酶联免疫吸附测定(ELISA)评估血清中游离DNA加合物8-OHdG的浓度。血清中发现的8-OHdG片段是氧化DNA损伤修复的一种特异性生物标志物。此外,使用硫代巴比妥酸反应性物质(TBARS)测定法评估接触DE动物大脑海马区脂质过氧化形式的氧化应激和损伤。在接触DE或对照气氛(过滤空气)1、3、12和24个月时评估这些终点。在所评估的DE浓度下,雄性或雌性大鼠在接触1、3、12或24个月后,在彗星试验中任何DNA损伤测量指标(尾部%DNA、尾长、尾矩或橄榄矩)方面,接触均无显著影响。接触组与对照组的比较以及1和3个月接触组按性别的比较显示血清8-OHdG浓度无显著差异(P>0.05)。3个月时所有接触组的8-OHdG浓度均高于其他任何时间点的接触组(P<0.05)。查看12个月和24个月组血清中8-OHdG水平,我们发现12个月组中、高水平与对照组有显著差异(P<0.05),以及一些其他分散的变化。在12个月高水平组中注意到性别差异(P<0.05)。然而,这些差异并不遵循接触依赖模式。所有其他比较均无显著差异(P>0.05)。以丙二醛(MDA)衡量的海马区TBARs浓度在接触不同水平DE的组和不同时间点显示出一些小的、分散的变化,但我们认为这些与接触无关。我们得出结论,这些大鼠接触DE不会导致脂质氧化损伤或DNA链断裂形式的损伤有任何显著增加。