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Induction of Oxidative Stress and Dysfunction of Nitric Oxide-Dependent Vascular Tone Caused by Quinones Contained in Diesel Exhaust Particles

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This article reviews studies of overproduction of reactive oxygen species during reductive activation of quinones contained in diesel exhaust particles. The resulting inhibition of nitric oxide synthase activity causing suppression of vasorelaxation by phenanthraquinone, one of the quinone in diesel exhaust particles, is also reviewed.
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... The toxicology associated with DEP has been attributed to the chemical properties of adsorbed species. For example, compounds found in DEP can induce oxidative stress (Kumagai and Shimojo, 2001; Li et al., 2002), cause vascular dysfunction (Kumagai and Shimojo, 2001), damage DNA (Kumagai et al., 1997), oxidize proximal protein thiols (Kumagai et al., 2002), and induce apoptosis (Hiura et al., 1999). Significantly, these studies utilized DEP extracts and do not consider possible effects associated with the DEP itself. ...
... The toxicology associated with DEP has been attributed to the chemical properties of adsorbed species. For example, compounds found in DEP can induce oxidative stress (Kumagai and Shimojo, 2001; Li et al., 2002), cause vascular dysfunction (Kumagai and Shimojo, 2001), damage DNA (Kumagai et al., 1997), oxidize proximal protein thiols (Kumagai et al., 2002), and induce apoptosis (Hiura et al., 1999). Significantly, these studies utilized DEP extracts and do not consider possible effects associated with the DEP itself. ...
... Among such compounds, quinones are often detected in atmospheric aerosol samples (König et al., 1983;Lewis et al., 1995;Allen et al., 1997;del Rosario Sienra and Rosazza, 2006;, sometimes with concentrations higher than 2 ng m -3 and are suspected to contribute to the toxicity of ambient particles. The toxic effects of quinones are often attributed to their ability to form reactive oxygen species (ROS) (Lemaire and Livingstone, 1997;Kumagai and Shimojo, 2001), but also for their mutagenicity (Chesis et al., 1984;Durant et al., 1996). ...
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... 50 Previous studies have confirmed that fine particle exposure generates reactive oxygen species (ROS). [51][52][53][54][55] The rises in ROS may be attributed to the decrease in PCs consisting of long PUFA chains observed in this study. This observation was consistent with the declines in plasmenylcholines because the vinyl ether bond is susceptible to ROS attack. ...
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... Among such compounds, quinones are often detected in atmospheric aerosol samples (König et al., 1983;Lewis et al., 1995;Allen et al., 1997;Cho et al., 2004;Shimmo et al., 2004;del Rosario Sienra and Rosazza, 2006;Jakober et al., 2006;Albinet et al., 2007Albinet et al., , 2008; Andreou and Rapsomanikis, 2009;Ringuet et al., 2012a) and are suspected to contribute to the toxicity of ambient particles. Their toxic effects are often attributed to their ability to form reactive oxygen species (ROS) (Lemaire and Livingstone, 1997;Kumagai and Shimojo, 2001), but also for their mutagenicity (Chesis et al., 1984;Durant et al., 1996;Pedersen et al., 2004Pedersen et al., , 2005. Recently, the IARC has classified 9,10-anthraquinone as a group 2B chemical, signifying its carcinogenic probability to humans (IARC, 2012) and highlighting the study of the fate of this compound. ...
... Among such compounds, quinones are often detected in atmospheric aerosol samples (König et al., 1983;Lewis et al., 1995;Allen et al., 1997;del Rosario Sienra and Rosazza, 2006;, sometimes with concentrations higher than 2 ng m -3 and are suspected to contribute to the toxicity of ambient particles. The toxic effects of quinones are often attributed to their ability to form reactive oxygen species (ROS) (Lemaire and Livingstone, 1997;Kumagai and Shimojo, 2001), but also for their mutagenicity (Chesis et al., 1984;Durant et al., 1996). ...
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... However, the chemicals associated with this toxicity remain uncharacterized. The study indicated that phenanthraquinone (a relatively abundant quinone in DEP) can act as a catalytic oxidizing agent for proximal protein sulfhydryls in addition to its ability to interact with NADPH-cytochrome P450 reductase, leading to the overproduction of reactive oxygen species (5,40). This chemical reactivity indicates that phenanthraquinone may be, at least partially, responsible for DEP-induced oxidative stress. ...
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Diesel exhaust particles (DEP) contain quinones that are capable of catalyzing the generation of reactive oxygen species in biological systems, resulting in induction of oxidative stress. In the present study, we explored sulfhydryl oxidation by phenanthraquinone, a component of DEP, using thiol compounds and protein preparations. Phenanthraquinone reacted readily with dithiol compounds such as dithiothreitol (DTT), 2,3-dimercapto-1-propanol (BAL), and 2,3-dimercapto-1-propanesulfonic acid (DMPS), resulting in modification of the thiol groups, whereas minimal reactivities of this quinone with monothiol compounds such as GSH, 2-mercaptoethanol, and N-acetyl-L-cysteine were seen. The modification of DTT dithiol caused by phenanthraquinone proceeded under anaerobic conditions but was accelerated by molecular oxygen. Phenanthraquinone was also capable of modifying thiol groups in pulmonary microsomes from rats and total membrane preparation isolated from bovine aortic endothelial cells (BAEC), but not bovine serum albumin (BSA), which has a Cys34 as a reactive monothiol group. A comparison of the thiol alkylating agent N-ethylmaleimide (NEM) with that of phenanthraquinone indicates that the two mechanisms of thiol modification are distinct. Studies revealed that thiyl radical intermediates and reactive oxygen species were generated during interaction of phenanthraquinone with DTT. From these findings, it is suggested that phenanthraquinone-mediated destruction of protein sulfhydryls appears to involve the oxidation of presumably proximal thiols and the reduction of molecular oxygen.
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