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Biomedical subjects

W A Pryor

Publications and source records attributed to W A Pryor.

At least 91 records · Page 5Linked to original sources

Aqueous extracts of cigarette tar containing the tar free radical cause DNA nicks in mammalian cells.

The ability of aqueous extracts of cigarette tar to nick DNA was investigated using viable mammalian cells. Tar extracts contain a radical with a stable electron spin resonance (ESR) signal at g = 2.0036 characteristic of a semiquinone. The association of the tar component that carries the ESR signal with DNA was demonstrated using viable rat alveolar macrophages. The formation of single-strand DNA breaks caused by cigarette tar extracts in viable rat thymocytes follows saturation kinetics, indicating a tar component associates with DNA and then nicks it. These studies support our hypothesis that tar components that contain the cigarette tar radical can enter cells, associate with, and then nick DNA.

Animals↗

Oxygen consumption and oxyradical production from microsomal reduction of aqueous extracts of cigarette tar.

Aqueous extracts of cigarette tar (ACT) contain a quinone-hydroquinone-semiquinone system that undergoes autoxidation to produce superoxide and hydrogen peroxide. In this paper we ask whether the production of activated oxygen species from this quinone system can be enhanced via an NAD(P)H-dependent autoxidation in which electrons are donated from electron transport components of the microsomal system to electron acceptors in ACT such as quinones and/or metal chelates. Therefore, the ability of ACT to enhance the oxidation of NADPH, consumption of oxygen, and production of oxyradicals during microsomal electron transport has been investigated. Rates of NADPH oxidation and oxygen consumption are enhanced in a concentration-dependent manner by both aqueous and dimethyl sulfoxide (DMSO) extracts of tar over that observed in the presence of microsomes alone. Over the time course studied, neither NADPH oxidation nor oxygen consumption by tar extracts is observed in the absence of microsomes. Microsomal NADPH oxidation is enhanced by 1,6- and 1,3-benzo[a]pyrene quinones and by iron-EDTA; per unit weight, the enhancement by these compounds is similar to that of tar. NADPH oxidation in the presence of tar and absence of iron-EDTA is inhibited by about 15% by the addition of deferoxamine to the reaction mixture. Chrysene quinone enhances NADPH oxidation to a much greater extent than does either of the benzo[a]pyrene quinones or tar. Inhibition of tar-stimulated microsomal oxygen uptake by superoxide dismutase, stimulation of oxygen uptake by azide (an inhibitor of catalase), and the presence of spin-trappable superoxide anion radical all indicate the reduction of tar components to superoxide and hydrogen peroxide. The similar effects of tar on NADPH oxidation catalyzed either by microsomes or by purified NADPH-cytochrome P450 reductase suggest that cytochrome P450 reductase is an important locus of electron transfer from microsomes to components of cigarette tar extracts. These data suggest that the cytotoxic and mutagenic effects of smoking may be mediated by metabolic activation of quinones and, to a lesser extent, metal chelates in cigarette tar to oxyradicals.

Animals↗

A kinetic model for the competitive reactions of ozone with amino acid residues in proteins in reverse micelles.

Lysozyme and 10 other proteins are solubilized in reverse micelles formed by 0.1 M sodium di-2-ethyl-hexylsulfosuccinate and 2.0-2.5 M water (pH 7.4) in isooctane solvent. Exposure of the protein-containing reverse micellar solutions to ozone causes oxidative damage to the proteins, as assessed by the oxidation of tryptophan residues. The oxidation product of the protein-bound tryptophan has a molar absorption coefficient of 3275 +/- 81 M-1 cm-1 (mean +/- S.D., n = 6) at 320 nm. The product is suggested to be a Criegee ozonide or a tautomer of the Criegee ozonide and not N-formylkynurenine. Ozonation of lysozyme in reverse micelles results in the formation of hydrogen peroxide in yields of only approximately 0.07 mol/mol of tryptophan residues oxidized. The recovery of hydrogen peroxide added as an internal standard to the lysozyme-containing reverse micellar solutions ranges from 84 to 88%, whether or not the samples are subjected to ozonation. This suggests that hydrogen peroxide is neither destroyed during the process of ozonation nor consumed by the protein to a significant extent in an adventitious reaction. A kinetic model for the overall reaction of ozone with the proteins is developed, taking into account the concentrations and the reactivities of individual amino acid residues toward ozone. The model predicts the fractional reaction of ozone with tryptophan residues in the proteins, despite differences in amino acid composition, molecular weight, and tertiary structures. The lack of influence of protein structure is confirmed further by the observation that the native lysozyme (with and without external S-carboxymethylcysteine) and S-carboxymethylated lysozyme give identical values of the fractional reaction of ozone with tryptophan residues. The kinetic equations for the competitive reactions of ozone with amino acid residues in proteins, with some minor modification, are applicable to ozonations on complex mixtures of lipids, proteins, and antioxidants.

Amino Acids↗

The identification of the allylic nitrite and nitro derivatives of methyl linoleate and methyl linolenate by negative chemical ionization mass spectroscopy.

The autoxidation of polyunsaturated fatty acids is initiated both in vivo and in vitro by nitrogen dioxide. The mechanism of the initiation process is believed to involve both addition reactions and hydrogen atom abstraction reactions, with hydrogen abstraction predominating at low levels of nitrogen dioxide. Therefore low levels of nitrogen dioxide should react with polyunsaturated fatty acids to give allylic derivatives; in an anaerobic system these derivations should be allylic nitro and nitrite compounds. Using negative methane chemical ionization mass spectrometry and other analytical techniques, we have identified these allylic nitrite and nitro compounds from the reactions of low levels of nitrogen dioxide with methyl linoleate and methyl linolenate in the absence of oxygen.

Chromatography, High Pressure Liquid↗

The ozonation of cholesterol: separation and identification of 2,4-dinitrophenylhydrazine derivatization products of 3 beta-hydroxy-5-oxo-5,6-secocholestan-6-al.

The ozonation products of cholesterol, which are of interest as possible biomarkers of O3 exposure, were studied by derivatization with 2,4-dinitrophenylhydrazine (DNPH). The DNPH derivatization of 3 beta-hydroxy-5-oxo-5,6-secocholestan-6-al (2) produces the expected trans (3b) and cis (3c) derivatives of 3 beta-hydroxy-5-oxo-5,6-secocholestan-6-al, and the unexpected DNPH derivative of 3,5-dihydroxy-B-norcholestane-6-carboxaldehyde (3a). The structures of 3a, 3b, and 3c were identified with 1H nuclear magnetic resonance (NMR), 13C NMR, DEPT, COSY, and H-C correlation two-dimensional NMR techniques, and by comparison with the spectra of known compounds. A possible mechanism involving an enamine functionality is proposed for the formation of 3a. The ratio of 3a/(3b + 3c) depends on the concentration of acid used and the reaction time.

Cholestanones↗

Cholesterol ozonation products as biomarkers for ozone exposure in rats.

Cholesterol, 1, which is present in both the lung lining fluid and cell membranes of lung tissue, reacts with ozone in aqueous systems to give 3 beta-hydroxy-5-oxo-5,6-secocholestan-6-al (2) as the major product. Reaction of 2 with 2,4-dinitrophenyl hydrazine (DNPH) in aqueous solutions, liposomes or lung extracts affords the anti and syn DNPH derivatives of 2 (3b and 3c) and of the rearrangement product 3,5-dihydroxy-B-norcholestane-6-carboxaldehyde (3a). These derivatives also are detected in lung tissue extracts from rats exposed to 1.3 ppm ozone for 12 hr.

1,2-Dipalmitoylphosphatidylcholine↗

Identification of heptanal and nonanal in bronchoalveolar lavage from rats exposed to low levels of ozone.

Heptanal and nonanal are identified from in vitro studies as potential biomarkers of exposure to ozone, the former resulting from ozonation of palmitoleic acid and the latter from oleic acid. An analytical method is developed based on derivatization using O-pentafluorobenzylhydroxylamine HCl and gas chromatography. These molecules also are present in the lung lavage of Sprague-Dawley rats exposed to 1.3 ppm ozone for 10 hr. These results suggest aldehydes may be useful dosimeters for ozone and indicate that unsaturated fatty acids in the lung lining fluid layer undergo ozonation in vivo.

Aldehydes↗

Ozonation of lysozyme in the presence of oleate in reverse micelles of sodium di-2-ethylhexylsulfosuccinate.

Ozone is shown to react with lysozyme in reverse micelles formed by 0.1 M sodium di-2-ethylhexylsulfosuccinate and 1.2-3 M water (pH 7.4) in isooctane solvent. The reaction of ozone is assessed by the oxidation of tryptophan residues in the protein to N-formylkynurenine. Cosolubilization of oleate in lysozyme-containing reverse micellar solutions at concentrations of 0.5-10 mM results in a progressive inhibition (19% to 82%) of the oxidation of tryptophan residues with a concentration for 50% inhibition around 2 mM. At this concentration of oleate, the magnitude of inhibition is independent of the micelle size and concentration, the overall interfacial area of reverse micelles, and the amount of ozone employed. These findings are discussed in terms of competitive reactions of ozone with unsaturated fatty acids and proteins in the lung lining fluid and in biological membranes.

Animals↗

Production of the Criegee ozonide during the ozonation of 1-palmitoyl-2-oleoyl-sn-glycero-3-phosphocholine liposomes.

It is likely that Criegee ozonides are formed in small amounts in the lungs of animals breathing ozone-containing air. This makes these compounds potential candidates to act as secondary toxins which relay the toxic effects of ozone deeper into lung tissue than ozone itself could penetrate. Therefore, we have determined the yields of Criegee ozonides from unsaturated lipids in liposomal systems as a model of the types of yields of Criegee ozonides that might be expected both in the lung lining fluid layer and in biological membranes. Ozonation of 1-palmitoyl-2-oleoyl-sn-glycero-3-phosphocholine liposomes produced both cis- and trans-Criegee ozonides. These ozonides have been isolated by solid phase extraction and high-performance liquid chromatography of the ozonized lipid, and the products have been identified by two-dimensional 1H nuclear magnetic resonance. The combined yield of the cis- and trans-Criegee ozonides is 10.7 +/- 2.8% (avg. +/- SD, n = 7) with small unilamellar liposomes and 10.6 +/- 2.7% (n = 3) with large multilamellar liposomes. We had previously reported (Chem. Res. Toxicol. 5, 505-511, 1992) that ozonation of methyl oleate in sodium dodecylsulfate micelles also produces an 11% yield of the Criegee ozonides. Thus, ozonation in a variety of models gives about 11% of the Criegee ozonide, suggesting that these products also would be formed in small but significant amounts in the lungs of animals breathing polluted air. Further research on the pharmacokinetics and possible toxicity of the Criegee ozonides of fatty acids is suggested.

Liposomes↗

Separation and spectral data of the six isomeric ozonides from methyl oleate.

The structures of the products obtained on ozonation of methyl oleate have been re-examined. The assignments for the six isomeric ozonides of methyl oleate have been made by 1H and 13C nuclear magnetic resonance (NMR), which were consistent with the retention times observed in high-performance liquid chromatography; the assignments were confirmed by mass and infrared spectroscopy. Two triplets for the ozonide ring protons of the cis and trans isomers in the normal (MOO1) and the two cross ozonides (MOO1 and MOO3) can be resolved by 400 MHz NMR. For MOO1 and MOO3, where the two ring carbons are equivalent, two peaks for the ring carbons of each cross ozonides are resolved in the 13C NMR spectra, one for the cis and one for the trans isomer. For MOO2, four peaks for the ring carbons are resolved in the 13C NMR spectra, two for the cis and two for the trans isomer.

Chromatography, High Pressure Liquid↗

Biological effects of cigarette smoke, wood smoke, and the smoke from plastics: the use of electron spin resonance.

This review compares and contrasts the chemistry of cigarette smoke, wood smoke, and the smoke from plastics and building materials that is inhaled by persons trapped in fires. Cigarette smoke produces cancer, emphysema, and other diseases after a delay of years. Acute exposure to smoke in a fire can produce a loss of lung function and death after a delay of days or weeks. Tobacco smoke and the smoke inhaled in a burning building have some similarities from a chemical viewpoint. For example, both contain high concentrations of CO and other combustion products. In addition, both contain high concentrations of free radicals, and our laboratory has studied these free radicals, largely by electron spin resonance (ESR) methods, for about 15 years. This article reviews what is known about the radicals present in these different types of smokes and soots and tars and summarizes the evidence that suggests these radicals could be involved in cigarette-induced pathology and smoke-inhalation deaths. The combustion of all organic materials produces radicals, but (with the exception of the smoke from perfluoropolymers) the radicals that are detected by ESR methods (and thus the radicals that would reach the lungs) are not those that arise in the combustion process. Rather they arise from chemical reactions that occur in the smoke itself. Thus, a knowledge of the chemistry of the smoke is necessary to understand the nature of the radicals formed. Even materials as similar as cigarettes and wood (cellulose) produce smoke that contains radicals with very different lifetimes and chemical characteristics, and mechanistic rationales for this are discussed. Cigarette tar contains a semiquinone radical that is infinitely stable and can be directly observed by ESR. Aqueous extracts of cigarette tar, which contain this radical, reduce oxygen to superoxide and thus produce both hydrogen peroxide and the hydroxyl radical. These solutions both oxidize alpha-1-proteinase inhibitor (a1PI) and nick DNA. Because of the potential role of radicals in smoke-inhalation injury, we suggest that antioxidant therapy (such as use of an inhaler for persons brought out of a burning building) might prove efficacious.

DNA Damage↗

How far does ozone penetrate into the pulmonary air/tissue boundary before it reacts?

A simple method is suggested for calculating the time it takes ozone to traverse a biological region, such as a bilayer or a cell, and comparing this time to the halflife of ozone within that region. For a bilayer the calculations suggest that most of the ozone reacts within a bilayer, but a fraction may exit unreacted. For the lung lining fluid layer (LLFL), the calculations show that ozone cannot cross this layer without reacting where the LLFL is thicker than about 0.1 microns. However, since the LLFL varies from 20 to 0.1 microns in thickness with patchy areas in the lower airways that are virtually uncovered, some ozone could reach underlying cells, particularly in the lower airways. For cells (such as alveolar type I epithelial cells), the calculations show that ozone reacts within the cell too rapidly to pass through and exit unreacted from the other side. These calculations have implications for ozone toxicity. In vivo, the toxicity of ozone is suggested to result from the effects of a cascade of products that are produced in the reactions of ozone with primary target molecules that lie close to the air/tissue boundary. These products, which have a lower reactivity and longer lifetime than ozone itself, can transmit the effects of ozone beyond the air/tissue interface. The variation in thickness of the LLFL may modulate the species causing damage to the cells below it. In the lower airways, where the LLFL is thin and patchy, more cellular damage may be caused by ozone itself; in the upper airways where the LLFL is thicker, secondary products (such as aldehydes and hydrogen peroxide) may cause most of the damage. In vitro studies must be designed in an attempt to model the lung physiology. For example, if cells in culture are studied, and if the cells are exposed to ozone while under a supporting medium solution that contains ozone-reactive substances, then the cells may be damaged by products that are formed in the reactions of ozone with the cell medium rather than by ozone itself.

Air Pollutants↗

Free radical generation in the brain precedes hyperbaric oxygen-induced convulsions.

We tested the hypothesis that hyperbaric oxygenation (HBO) generates free radicals in the brain before the onset of neurological manifestations of central nervous system (CNS) oxygen poisoning. Chronically cannulated, conscious rats were individually placed in a transparent pressure chamber and exposed to (1) 5 atmospheres absolute (ATA) oxygen for 15 min (n = 4); (2) 5 ATA oxygen for 30 min (n = 5), during which no visible convulsions occurred; (3) 5 ATA oxygen for 30 min with recurrent convulsions (n = 6); (4) 5 ATA oxygen until the appearance of the first visible convulsions (n = 5); (5) 4 ATA oxygen for 60 min during which no convulsions occurred (n = 5); and (6) 5 ATA air for 30 min (n = 5, controls). Immediately before compression, 1 mL of 0.1 M of alpha-phenyl-N-tert-butyl nitrone (PBN) was administered intravenously (iv) for spin trapping. At the termination of each experiment, rats were euthanized by pentobarbital iv and decompressed within 1 min. Brains were rapidly removed for preparation of lipid extracts (Folch). The presence of PBN spin adducts in the lipid extracts was examined by electron spin resonance (ESR) spectroscopy. ESR spectra from unconvulsed rats exposed to 5 ATA oxygen for 30 min revealed both oxygen-centered and carbon-centered PBN spin adducts in three of the five brains. One of the five rats in this group showed an ascorbyl signal in the ESR spectrum.(ABSTRACT TRUNCATED AT 250 WORDS)

Animals↗

The inhibitory effect of extracts of cigarette tar on electron transport of mitochondria and submitochondrial particles.

Acetonitrile extracts of cigarette tar inhibit state 3 and state 4 respiration of intact mitochondria. Exposure of respiring submitochondrial particles to acetonitrile extracts of cigarette tar results in a dose-dependent inhibition of oxygen consumption and reduced nicotinamide adenine dinucleotide (NADH) oxidation. This inhibition was not due to a solvent effect since acetonitrile alone did not alter oxygen consumption or NADH oxidation. Intact mitochondria are less sensitive to extracts of tar than submitochondrial particles. The NADH-ubiquinone (Q) reductase complex is more sensitive to inhibition by tar extract than the succinate-Q reductase and cytochrome complexes. Nicotine or catechol did not inhibit respiration of intact mitochondria. Treatment of submitochondrial particles with cigarette tar results in the formation of hydroxyl radicals, detected by electron spin resonance (ESR) spin trapping. The ESR signal attributable to the hydroxyl radical spin adduct requires the presence of NADH and is completely abolished by catalase and to a lesser extent superoxide dismutase (SOD). Catalase and SOD did not protect the mitochondrial respiratory chain from inhibition by tar extract, indicating that the radicals detected by ESR spin trapping are not responsible for the inhibition of the electron transport. We propose that tar causes at least two effects: (1) Tar components interact with the electron transport chain and inhibit electron flow, and (2) tar components interact with the electron transport chain, ultimately to form hydroxyl radicals.

Acetonitriles↗

tert-Butyl hydroperoxide-induced radical production in rat liver mitochondria.

When rat liver mitochondria are treated with tert-butyl hydroperoxide (TBHP) in the presence of the spin trap 5,5-dimethyl-1-pyrroline N-oxide (DMPO), electron paramagnetic resonance (EPR) signals are detected attributable to spin adducts resulting from the trapping of methyl, tert-butoxyl, and tert-butylperoxyl radicals. The addition of respiratory substrate results in a 3- to 7.5-fold increase in the signal intensity of the DMPO/methyl adduct, no change in the signal intensity of the DMPO/tert-butoxyl adduct, and complete loss of the DMPO/tert-butylperoxyl adduct signal. The magnitude of increase of methyl radical production in the presence of respiratory substrate is related to the respiratory control ratio (RCR) of the mitochondrial preparation. In the presence of antimycin A, which blocks electron flow between cytochromes b and c1, no stimulation of methyl radical production is detected with respiratory substrate. Stimulation of methyl radical production by the addition of respiratory substrate is detected in cytochrome c-depleted mitochondria. A similar increase in methyl radical production is detected when ferrous cytochrome c is treated with TBHP in the presence of DMPO (as compared to when ferricytochrome c is used). These results indicate that TBHP is reduced directly by either cytochrome c1, cytochrome c, or by both of these electron transport chain components in mitochondria undergoing state 4 respiration.

3-Hydroxybutyric Acid↗