Enhancement of 2′-deoxyguanosine hydroxylation and DNA damage by coal and oil fly ash in relation to particulate metal content and availability

被引:38
作者
Prahalad, AK
Inmon, J
Ghio, AJ
Gallagher, JE
机构
[1] US EPA, Natl Hlth & Environm Effects Res Lab, Human Studies Div, Res Triangle Pk, NC 27711 USA
[2] Univ N Carolina, Curriculum Toxicol, Chapel Hill, NC 27599 USA
关键词
D O I
10.1021/tx000110j
中图分类号
R914 [药物化学];
学科分类号
100701 ;
摘要
Epidemiologic studies have shown causal relationships between air pollution particles and adverse health effects in susceptible subpopulations. Fly ash particles (containing water-soluble and insoluble metals) are a component of ambient air particulate pollution and may contribute to particulate-induced health, effects. Some of the pathological effects after inhalation of the particles may be due to reactive oxygen species (ROS) produced by metal-catalyzed reactions. In this investigation, we analyzed emission source particulates oil fly ash (OFA) and coal fly ash (CFA) for metal content and solubility in relation to their ability to induce 2'-deoxyguanosine (dG) hydroxylation and DNA damage as measured by 8-oxo-dG formation by HPLC/UV-electrochemical detection (ECD). Water-soluble vanadium and nickel were present at the highest concentrations, and iron was present in trace amounts in OFA (5.1% V, 1.0% Ni, and 0.4% Fe by weight), In contrast, CFA comprised mostly of water-insoluble aluminosilicates and iron (9.2% Al, 12.2% Si, and 2.8% Fe by weight). As a first approach to gain insight into the mode of action of these particulates, we examined metal species-catalyzed kinetics of dG hydroxylation. Metal species at a concentration of 0.1 mM in the incubation mixture containing 0.1 mM dG under ambient air at room temperature catalyzed maximum 8-oxo-dG formation at 15 min with yields ranging from 0.05 to 0.17%, decreasing in the following order: vanadium(IV) > iron(II) > vanadium(V) > iron(III) greater than or equal to nickel(II). Insoluble Fe(III) oxide (Fe2O3) under similar conditions had no effect. Consistent with these results, OFA rich in vanadium and nickel concentrations showed a dose-dependent increase in the level of dG hydroxylation to 8-oxo-dG; formation at particulate concentrations of 0.1-1 mg/mL (p < 0.05). In contrast, CFA with high concentrations of aluminosilicates and iron did not result in a significant increase in the level of 8-oxo-dG over that of the control, i.e., dG (p > 0.05). DMSO, a (OH)-O-. scavenger, inhibited OFA-induced 8-oxo-dG formation, and metal ion chelators, deferoxamine (DFX), DTPA, and ferrozine blocked OFA-induced 8-oxo-dG formation. OFA and CFA induced 8-oxo-dG formation in a pattern similar to that observed for dG hydroxylation when calf thymus DNA was used as a substrate. Treatment of OFA particles with DFX before reacting with DNA or addition of a catalase in the incubation mixture significantly suppressed 8-oxo-dG formation (p < 0.05). These results suggest that metal availability, but not the concentration of metals present in CFA and OFA, is critical in mediating molecular oxygen-dependent dG; hydroxylation and DNA base damage.
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页码:1011 / 1019
页数:9
相关论文
共 49 条
[21]   In vivo evidence of free radical formation in the rat lung after exposure to an emission source air pollution particle [J].
Kadiiska, MB ;
Mason, RP ;
Dreher, KL ;
Costa, DL ;
Ghio, AJ .
CHEMICAL RESEARCH IN TOXICOLOGY, 1997, 10 (10) :1104-1108
[22]   HYDROXYLATION OF DEOXYGUANOSINE AT THE C-8 POSITION BY ASCORBIC-ACID AND OTHER REDUCING AGENTS [J].
KASAI, H ;
NISHIMURA, S .
NUCLEIC ACIDS RESEARCH, 1984, 12 (04) :2137-2145
[23]  
KASAI H, 1984, JPN J CANCER RES, V75, P841
[24]  
KASPRZAK KS, 1989, CANCER RES, V49, P5964
[25]  
KASPRZAK KS, 1991, CHEM RES TOXICOL, V4, P604, DOI 10.1021/tx00024a002
[26]  
KINLEN LJ, 1988, BRIT J IND MED, V45, P219
[27]  
KRAUS T, 1989, ZBL HYG UMWELTMED, V188, P108
[28]   MISREADING OF DNA TEMPLATES CONTAINING 8-HYDROXYDEOXYGUANOSINE AT THE MODIFIED BASE AND AT ADJACENT RESIDUES [J].
KUCHINO, Y ;
MORI, F ;
KASAI, H ;
INOUE, H ;
IWAI, S ;
MIURA, K ;
OHTSUKA, E ;
NISHIMURA, S .
NATURE, 1987, 327 (6117) :77-79
[29]   MUTAGENICITY, CARCINOGENICITY AND TERATOGENICITY OF VANADIUM COMPOUNDS [J].
LEONARD, A ;
GERBER, GB .
MUTATION RESEARCH, 1994, 317 (01) :81-88
[30]   VANADATE-STIMULATED OXIDATION OF NAD(P)H IN THE PRESENCE OF BIOLOGICAL-MEMBRANES AND OTHER SOURCES OF O-2- [J].
LIOCHEV, SI ;
FRIDOVICH, I .
ARCHIVES OF BIOCHEMISTRY AND BIOPHYSICS, 1990, 279 (01) :1-7