Part 3. Assessment of genotoxicity and oxidative damage in rats after chronic exposure to new-technology diesel exhaust in the ACES bioassay.

Lance M Hallberg, Jonathan B Ward, Caterina Hernandez, Bill T Ameredes, Jeffrey K Wickliffe
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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). 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Abstract

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.

第3部分。在ACES生物测定中评估大鼠长期暴露于新技术柴油废气后的遗传毒性和氧化损伤
2001年,美国环境保护署(EPA*)和加州空气资源委员会(CARB)采用了柴油燃料和重型柴油发动机排放的新标准。到2007年,柴油发动机必须满足这些新的颗粒物(PM)标准,并遵循其他标准。通过结合先进的压缩点火发动机技术、废气后处理系统的发展以及燃料的重新配制,引入了严格的标准。在美国环保署实施2007年标准之前,与柴油废气(DE)接触有关的人类健康影响与柴油燃料溶剂和燃烧成分有关。在早期的研究中,柴油发动机排气成分反过来又与鼠伤寒沙门氏菌和哺乳动物细胞培养物的突变性增加有关(Tokiwa和Ohnishi 1986)。此外,DE被证明会增加啮齿动物的肿瘤发生率和诱导8-羟基脱氧鸟苷(8-OHdG)加合物(Ichinose et al. 1997)以及大鼠的总DNA加合物(Bond et al. 1990)。此外,DE是由多环芳烃(PAHs)和颗粒物的复杂混合物组成的。其中一种多环芳烃,3-硝基苯并蒽醌(3-NBA),也存在于城市空气中。已经观察到3-NBA可以诱导人肝癌细胞DNA中的微核形成(Lamy et al. 2004)。目前的研究是高级协同排放研究(ACES)的一部分,这是一个由健康影响研究所和协调研究委员会开展的多学科项目。其目的是确定最近重型柴油发动机的工程改进是否减少了与接触DE成分有关的毒性。为此,我们对长期暴露于符合2007年标准的柴油发动机(新技术柴油排气,或NTDE)的DE长达24个月的Wistar Han大鼠的血清和组织进行了生物测定,评估了潜在的遗传毒性和氧化应激诱导。基因毒性是通过肺组织中DNA链断裂来测量的,使用碱修饰的彗星测定法。作为在彗星试验中评估可能的DNA损伤的相关性,游离DNA加合物8-OHdG的浓度通过竞争性酶联免疫吸附试验(ELISA)在血清中进行评估。在血清中发现的8-OHdG片段是氧化DNA损伤修复的特异性生物标志物。此外,采用硫代巴比妥酸反应性物质(TBARS)测定来评估de暴露动物大脑海马区氧化应激和脂质过氧化形式的损伤。这些终点在暴露于DE或对照空气(过滤空气)1、3、12和24个月时进行评估。在评估的DE浓度下,在1、3、12或24个月后,暴露在雄性或雌性大鼠的彗星试验中的任何DNA损伤测量(尾巴DNA百分比、尾巴长度、尾巴时刻或橄榄时刻)中都没有显着影响。暴露1个月和3个月时,暴露组与对照组和性别组比较,血清8-OHdG浓度差异无统计学意义(P > 0.05)。各暴露组3个月时8-OHdG浓度均高于其他暴露组(P < 0.05)。观察12个月组和24个月组的血清8-OHdG水平,我们发现12个月组在中高水平上与对照组有显著差异(P < 0.05),以及其他一些零散的变化。12个月高水平组存在性别差异(P < 0.05)。然而,这些差异并不遵循暴露依赖模式。其他比较均无统计学意义(P > 0.05)。以丙二醛(MDA)测量的海马TBARs浓度在暴露于不同水平DE和不同时间点的组中显示出一些小而分散的变化,但我们不认为这些变化与暴露有关。我们得出的结论是,这些大鼠暴露于DE并没有显著增加对脂质的氧化损伤或以链断裂形式对DNA的损伤。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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