Autoxidation of methyl linoleate initiated by the ozonide of allylbenzene.

Allylbenzene ozonide (ABO), a model for polyunsaturated fatty acid (PUFA) ozonides, initiates the autoxidation of methyl linoleate (18:2 ME) at 37 degrees C under 760 torr of oxygen. This process is inhibited by d-alpha-tocopherol (alpha-T) and 2,6-di-tert-butyl-4-methylphenol (BHT). The autoxidation was followed by the appearance of conjugated diene (CD), as well as by oxygen-uptake. The rates of autoxidation are proportional to the square root of ABO concentration, implying that the usual free radical autoxidation rate law is obeyed. Activation parameters for the thermal decomposition of ABO were determined under N2 in the presence of radical scavengers and found to be Ea = 28.2 +/- 0.3 kcal mol-1 and log A = 13.6 +/- 0.2; kd (37 degrees C) is calculated to be (5.1 +/- 0.3) X 10(-7) sec-1. Autoxidation data are also reported for ozonides of 18:2 ME and methyl oleate (18:1 ME).

Toxicity of polycyclic aromatic hydrocarbons. VI. Effects of 1-nitropyrene on serum enzyme levels in rats, and protection against it by beta-naphthoflavone and dimethyl sulfoxide.

Male Sprague-Dawley rats were pretreated i.p. with corn oil or DMSO (1.5 ml/kg/day), or with beta-naphthoflavone (BNF, 40 mg/kg/day) in corn oil or DMSO for 3 days. 1-Nitropyrene (1-NP, 150 mg/kg) in DMSO was injected i.p. 24 hr after pretreatment. A significant increase in the levels of several serum enzymes was seen in rats pretreated with corn oil alone 24 hr after 1-NP injection. The increase in enzyme activities was significantly reduced by a 3-day pretreatment with DMSO or BNF.

Toxicity of aromatic hydrocarbons. VII. Hepatotoxicity of 9-nitrophenanthrene, and protection against it by beta-naphthoflavone.

Male Sprague-Dawley rats were treated with a single i.p. injection of DMSO (3.0 ml/kg) or 9-nitrophenanthrene (9-NP, mg/kg) in DMSO. 9-NP produced a significant elevation of serum aspartate aminotransferase, alanine aminotransferase, sorbitol dehydrogenase, and gamma-glutamyl transpeptidase (GGTP) levels relative to DMSO-injected rats 24 hr after injection. With the exception of GGTP, the increase in enzyme activities induced by 9-NP was significantly reduced by a 3-day pretreatment with beta-naphthoflavone (BNF; 40 mg/kg/day) in DMSO. The effect of 9-NP on GGTP levels was enhanced by BNF pretreatment.

Toxicity of polycyclic aromatic hydrocarbons. V. Protective effect of beta-naphthoflavone against hepatotoxicity induced by diphenaldehyde in rats.

Male Sprague-Dawley rats were treated ip with beta-naphthoflavone (40 mg/kg/day) in corn oil or in DMSO for three days. Diphenaldehyde (90 mg/kg in DMSO) was injected ip 24 hr after pretreatment. The increase in the levels of aspartate aminotransferase, alanine aminotransferase, sorbitol dehydrogenase, gamma glutamyl transpeptidase, and lactate dehydrogenase was significantly lower in rats pretreated with BNF. This suggests that the BNF-induced P-450 isozyme systems have a protective effect against the acute hepatotoxicity of diphenaldehyde.

Toxicity of polycyclic aromatic hydrocarbons. IV. Effects of diphenaldehyde, a major product of ozonized phenanthrene, in rats.

Diphenaldehyde is the major product of phenanthrene ozonized on silica gel. Male Sprague-Dawley rats were treated with a single ip injection of DMSO (3.0 ml/kg) or diphenaldehyde (90 mg/kg) in DMSO. Diphenaldehyde produced significant alterations in levels of serum aspartate aminotransferase, alanine aminotransferase, sorbitol dehydrogenase, gamma-glutamyl transpeptidase, and lactate dehydrogenase relative to DMSO-injected rats 24 hr after injection. These results, as well as gross observations on necropsy, suggest that diphenaldehyde exhibits significant hepatotoxicity.

Toxicity of polycyclic aromatic hydrocarbons. III. Effects of beta-naphthoflavone pretreatment on hepatotoxicity of compounds produced in the ozonation or NO2-nitration of phenanthrene and pyrene in rats.

Male Sprague-Dawley rats were treated ip with beta-naphthoflavone (BNF, 40 mg/kg/day) in dimethylsulfoxide (DMSO, 26.7 mg BNF/ml) for three days. At 24 hr after the pretreatment DMSO (3.0 ml/kg), phenanthrene (150 mg/kg), ozonized or nitrated products of phenanthrene (150 mg/kg), pyrene (150 mg/kg), or ozonized or nitrated products of pyrene (150 mg/kg) were injected ip. Phenanthrene, pyrene, and their ozonized or nitrated products were dissolved in DMSO (50 mg/ml). No increase in the level of aspartate aminotransferase (AST), alanine aminotransferase (ALT) or sorbitol dehydrogenase (SDH) was seen in the pretreated rats 48 hr after the treatment. This is in contrast to what was seen in previous work without the BNF pretreatment. BNF pretreatment induced a small but significant increase in gamma-glutamyl transpeptidase (GGTP) levels. No treatment group receiving BNF differed from another with respect to GGTP. A decrease in lactate dehydrogenase (LDH) levels was noted in the nitro-PAH treatment groups; the same phenomenon was observed earlier in rats treated with nitro-PAH without BNF treatment. These results suggest that the mixed-function oxidase systems specifically induced by BNF have a protective effect against the hepatotoxicity of the oxonized or nitrated products of phenanthrene and pyrene.

Toxicity of polycyclic aromatic hydrocarbons. II. Effect of NO2-nitrated phenanthrene and pyrene on blood chemistry in rats.

Male Sprague-Dawley rats were treated with a single ip injection of dimethyl sulfoxide (DMSO), phenanthrene, nitrated products of phenanthrene, pyrene, or nitrated products of pyrene. Phenanthrene, pyrene and their nitrated products were dissolved in DMSO. Phenanthrene produced a significant elevation of serum aspartate aminotransferase (AST) and alanine aminotransferase (ALT) levels relative to DMSO-injected rats 24 hr after injection. Gamma-glutamyl transpeptidase (GGTP) levels were significantly increased for groups treated with phenanthrene when compared with the DMSO group 72 hr after injection. Nitrated products of phenanthrene produced a significant elevation of serum AST, ALT, sorbitol dehydrogenase (SDH), and GGTP levels when compared with groups treated with DMSO and phenanthrene 24 hr after injection. Four of six rats in the nitrated phenanthrene treatment group died between 48 and 72 hr after the injection. Injection of pyrene caused no significant increases in serum enzyme activities. Significant changes in the serum AST, SDH and LDH levels were observed with the nitrated products of pyrene at 24 hr. Only SDH levels were significantly different when pyrene and its nitrated products were compared. No significant differences were detected at 72 hr with the nitrated products of pyrene. As supported by serum chemistry, this study suggests that the products of the reaction of NO2 with two model polynuclear aromatic hydrocarbons (PAH) are hepatotoxic. Both pyrene and phenanthrene form nitrated products that are more toxic than the parent PAH, but the nitrated products of phenanthrene appear to be more toxic than the nitration products of pyrene.

A comparison of the rates of ozonation of biological antioxidants and oleate and linoleate esters.

The rates of reaction with ozone of some biological antioxidants and simple polyunsaturated fatty acids (PUFA) have been measured in water or in aqueous micellar solutions. At pH 7.0 the rate constants are ca. 10(6) M-1 sec-1 for urate, alpha-tocopherol, and PUFA, and 6 X 10(7) M-1 sec-1 for ascorbate. When ozone-containing air is breathed, ascorbate in the lung may undergo direct ozonation. However, alpha-tocopherol is probably spared direct reaction with ozone because it doesn't effectively compete with PUFA in pulmonary membranes; rather, tocopherol is used to scavenge radicals produced from the ozone-PUFA reaction.

Toxicity of polycyclic aromatic hydrocarbons. I. Effect of phenanthrene, pyrene, and their ozonized products on blood chemistry in rats.

Male Sprague-Dawley rats were treated with a single ip injection of physiological saline (3.0 ml/kg), dimethyl sulfoxide (DMSO, 3.0 ml/kg), phenanthrene (150 mg/kg), ozonized products of phenanthrene (150 mg/kg), pyrene (150 mg/kg), or ozonized products of pyrene (150 mg/kg). Phenanthrene, pyrene, and their ozonized products were dissolved in DMSO (50 mg/ml). Serum aspartate aminotransferase (AST) activity was increased significantly 24 hr after ip administration of DMSO when compared with physiological saline. Phenanthrene produced a significant elevation of serum AST and gamma-glutamyl transpeptidase (GGTP) levels related to physiological saline and DMSO-injected rats 24 hr after injection. However, GGTP levels for groups treated with DMSO or phenanthrene were not significantly increased when compared with saline groups 72 hr after injection. Ozonized products of phenanthrene produced a significant elevation of serum AST, alanine aminotransferase (ALT), GGTP, and bilirubin levels when compared with groups treated with physiological saline, DMSO, and phenanthrene 24 or 72 hr after injections. The ozonized products of phenanthrene also produced significant elevation of serum creatinine levels compared with physiological saline, DMSO, and phenanthrene groups at 24 hr after treatment and of blood urea nitrogen (BUN) levels at 24 and 72 hr. Although pyrene caused a small but significant increase in the serum AST and bilirubin levels 24 hr after treatment, no significant change in the serum AST, ALT, GGTP, BUN, and creatine levels were observed with the ozonized products of pyrene at 24 or 72 hr. This study demonstrates significant alterations in serum chemistry induced by reaction products of ozone with phenanthrene. No such effect was observed when the products of pyrene ozonation were administered. Although the ozonation products of pyrene were not toxic under the conditions of this study, phenanthrene products were more hepatotoxic than was phenanthrene itself. Nephrotoxicity was also an apparent effect of ozonized phenanthrene. Since ozone-polycyclic aromatic hydrocarbon (PAH) reactions may occur in the atmosphere, these reactions might produce compounds that are more toxic than either ozone or the PAH alone.