Source-dependent variation in hydroxyl radical production by airborne particulate matter

被引:41
作者
Alaghmand, Marjan [1 ]
Blough, Neil V. [1 ]
机构
[1] Univ Maryland, Dept Chem & Biochem, College Pk, MD 20742 USA
关键词
D O I
10.1021/es061902o
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Epidemiological studies suggest exposure to airborne particles is responsible for a wide range of adverse health effects, potentially arising from particle-induced oxidative stress. A highly sensitive fluorescence method was employed to measure the production of hydroxyl radical by a broad range of particle types including urban dust, diesel particulate matter, coal fly ash, kaolinite, and silica. Little or no production of (OH)-O-center dot was observed in the absence of an added electron donor or H2O2. In the presence of a biological electron donor (NADPH, 3 mM), the rate of (OH)-O-center dot production (R-OH) for 3 mg/mL of these particles varied from 23 nM s(-1) for diesel particulate matter (SRM 2975) to 0.20 nM s(-1) for coal fly ash (SRM 2689). No detectable (OH)-O-center dot was produced by kaolinite or silica. Hydroxyl radical formation was eliminated under anaerobic conditions and in the presence of catalase, indicating that O-2 and H2O2 are required for its generation. Partial inhibition of (OH)-O-center dot formation by superoxide dismutase (SOD) was also observed in some cases, suggesting that superoxide (O-2(center dot-)) is also involved. The metal chelator deferoxamine mesylate (DFX) in most cases suppressed (OH)-O-center dot formation, but diethylenetriaminepentaacetic acid (DTPA) generally enhanced it, implicating metal ion reactions in (OH)-O-center dot generation as well. The dependence of R-OH on NADPH concentration further implicates particle surface reactions in (OH)-O-center dot formation. To our knowledge, these measurements provide the first quantitative estimate of R-OH for a broad range of particle types.
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页码:2364 / 2370
页数:7
相关论文
共 49 条
[1]   Metal composition and solubility determine lung toxicity induced by residual oil fly ash collected from different sites within a power plant [J].
Antonini, JM ;
Taylor, MD ;
Leonard, SS ;
Lawryk, NJ ;
Shi, XL ;
Clarke, RW ;
Roberts, JR .
MOLECULAR AND CELLULAR BIOCHEMISTRY, 2004, 255 (1-2) :257-265
[2]   CHEMICALLY MEDIATED FLUORESCENCE YIELD SWITCHING IN NITROXIDE FLUOROPHORE ADDUCTS - OPTICAL SENSORS OF RADICAL REDOX REACTIONS [J].
BLOUGH, NV ;
SIMPSON, DJ .
JOURNAL OF THE AMERICAN CHEMICAL SOCIETY, 1988, 110 (06) :1915-1917
[3]  
BRIEDE JJ, 2005, ENVIRON SCI TECHNOL, V39, P2947
[4]   Air pollution and cardiovascular disease - A statement for healthcare professionals from the expert panel on population and prevention science of the American Heart Association [J].
Brook, RD ;
Franklin, B ;
Cascio, W ;
Hong, YL ;
Howard, G ;
Lipsett, M ;
Luepker, R ;
Mittleman, M ;
Samet, J ;
Smith, SC ;
Tager, I .
CIRCULATION, 2004, 109 (21) :2655-2671
[5]   Are we sure we know how to measure 8-oxo-7,8-dihydroguanine in DNA from human cells? [J].
Collins, AR ;
Cadet, J ;
Möller, L ;
Poulsen, HE ;
Viña, J .
ARCHIVES OF BIOCHEMISTRY AND BIOPHYSICS, 2004, 423 (01) :57-65
[6]   HYDROXYL RADICAL GENERATION BY COAL-MINE DUST - POSSIBLE IMPLICATION TO COAL-WORKERS PNEUMOCONIOSIS (CWP) [J].
DALAL, NS ;
NEWMAN, J ;
PACK, D ;
LEONARD, S ;
VALLYATHAN, V .
FREE RADICAL BIOLOGY AND MEDICINE, 1995, 18 (01) :11-20
[7]   Role of free radicals in the toxicity of airborne fine particulate matter [J].
Dellinger, B ;
Pryor, WA ;
Cueto, R ;
Squadrito, GL ;
Hegde, V ;
Deutsch, WA .
CHEMICAL RESEARCH IN TOXICOLOGY, 2001, 14 (10) :1371-1377
[8]   ELECTRON-SPIN RESONANCE CHARACTERIZATION OF RADICALS FROM 3,4-DIHYDROXYPHENYLALANINE - SEMI-QUINONE ANIONS AND THEIR METAL-CHELATES [J].
FELIX, CC ;
SEALY, RC .
JOURNAL OF THE AMERICAN CHEMICAL SOCIETY, 1981, 103 (10) :2831-2836
[9]  
FINKELSTEIN E, 1979, MOL PHARMACOL, V16, P676
[10]   Comparison of gas-phase free-radical populations in tobacco smoke and model systems by HPLC [J].
Flicker, TM ;
Green, SA .
ENVIRONMENTAL HEALTH PERSPECTIVES, 2001, 109 (08) :765-771