Metabolism of 1-(4-hydroxy-3-methoxyphenyl)-2-propanone, a smoke flavour ketone, in rat

1. Metabolites of 1-(4-hydroxy-3-methoxyphenyl)-2-propanone (HMP-one), a smoke flavour compound, were isolated from rat urine using hydrolysis, ether extraction, t.l.c. and g.l.c. 2. Three metabolites were identified by mass spectrometry and independent synthesis, namely: 1-(3, 4-dihydroxyphenyl)-2-propanone (Met I), 1-(3, 4-dihydroxyphenyl)-2-propanol (Met II), and 1-(4-hydroxy-3-methoxyphenyl)-2-propanol (Met III). 3. A g.l.c. method for the quantitative determination of the parent compound and metabolites in urine was devised. Unchanged HMP-one accounted for about 74% dose, with Met I 11%, Met II 5%, and Met III 9%. All compounds were excreted both as sulphate and glucuronide conjugates.

Effects of carbon tetrachloride, menadione, and paraquat on the urinary excretion of malondialdehyde, formaldehyde, acetaldehyde, and acetone in rats

Excretions of the lipid peroxidation products, formaldehyde (FA), acetaldehyde (ACT), malondialdehyde (MDA), and acetone (ACON), were simultaneously identified and quantitated in the urine of female Sprague-Dawley rats by gas chromatography-mass spectroscopy (GC-MS) and high pressure liquid chromatography (HPLC) following the acute administration of carbon tetrachloride, a model alkylating agent that does not induce glutathione depletion, and the redox cycling compounds paraquat and menadione. All three xenobiotics are well-known inducers of oxidative stress. Oxidative stress was induced by oral administration of single doses of 2.5 mL of carbon tetrachloride/kg, 60 mg menadione/kg, and 75 mg paraquat/kg. These doses are approximately 50% of the LD50's for the three xenobiotics. Urinary excretion of FA, ACT, MDA, and ACON increased relative to control animals following treatment with all xenobiotics. Over the 48 hours of the study, the greatest increases in the excretion of MDA, FA, ACT, and ACON occurred after paraquat administration, with increases of approximately 2.7-, 2.6-, 4.3-, and 11.0-fold, respectively. This technique may have wide-spread applicability as an effective biomarker for investigating altered lipid metabolism in disease states and exposure to environmental pollutants/xenobiotics.

Excretion of malondialdehyde, formaldehyde, acetaldehyde and acetone in the urine of rats following acute and chronic administration of ethanol

Recent studies have shown that xenobiotics which induce oxidative stress result in an increased production and excretion of acetaldehyde (ACT), formaldehyde (FA), acetone (ACON) and malondialdehyde (MDA) in the urine of rats. We have therefore examined the effect of acute and chronic ethanol administration on the excretion of these four lipid metabolites in female Sprague-Dawley rats. Urine samples were collected over dry ice for 6 hr time periods. Aliquots of urine were derivatized with 2,4-dinitrophenylhydrazine HCl, and extracted with n-pentane. High pressure lipid chromatogrpahy (HPLC) was used to quantitate and the hydrazones of the four lipid metabolite products. Following a single, oral, acute dose of 5 g ethanol/kg, urinary excretion of ACT increased approximately 5.8-fold from 6 to 12 hr posttreatment, and decreased thereafter. FA excretion decreased by approximately 50% from 0 to 12 hr, returned to control values in the 18-24 hr urine samples, and was 1.3-fold greater than control values at 42-48 hr. ACON increased 3.1-fold over control values from 0 to 30 hr and remained elevated throughout the remaining 18 hr of the study. The excretion of MDA increased approximately 1.5-fold from 18 to 36 hr, then remained constant through the 48 hr time point. In a separate series of experiments, a chronic oral dose of 0.5 g ethanol/kg was administered to rats for 10 consecutive days and the urinary excretion of the lipid metabolites MDA, FA, ACT and ACON was examined for 11 days, beginning with the first day of ethanol administration.(ABSTRACT TRUNCATED AT 250 WORDS)

Biological monitoring of workers exposed to styrene and acetone

Twenty-two workers exposed to styrene and acetone in two fiberglass industries were monitored on Monday and Thursday for 8 hours using passive dosimeters. Urine samples were collected at the end of the workshift and before the start of the work on the next morning (Tuesday and Friday). The charcoal disks of the passive dosimeters were analysed by gas-chromatography. Mandelic acid (MA) and phenylglyoxylic acid (PGA) were measured using a HPLC method; values were expressed in mg/g of creatinine. The 8-h TWA exposure values for styrene and acetone ranged respectively from 22 to 522 mg/m3 and 40-1581 mg/m3 on Monday; 25-423 mg/m3 and 55-579 mg/m3 on Thursday. Styrene TWA exposure values significantly correlate with the sum of metabolites at the end of workday (r = 0.70 on Monday and r = 0.95 on Thursday) and also at the next morning (r = 0.86 on Tuesday and r = 0.85 on Friday). A styrene exposure level of 213 mg/m3 (ACGIH-TLV) was associated with an excretion of metabolites (MA+PGA) higher on Thursday (803 mg/g creat) than on Monday (570 mg/g creat). The same result was found on Friday (459 mg/g creat) compared with Tuesday (305 mg/g creat). Moreover our data show that the simultaneous exposure to acetone does not modify the excretion of MA. In conclusion the TLV of styrene is associated with different values of metabolites at the beginning and at the end of the work-week.

Endrin-induced urinary excretion of formaldehyde, acetaldehyde, malondialdehyde and acetone in rats

Previous studies have shown that endrin induces an oxidative stress in rats as demonstrated by an increase in hepatic lipid peroxidation, a decrease in glutathione content and a decrease in the activity in selenium-dependent glutathione peroxidase. We have therefore examined the effects of orally administering 1.5, 3.0, 4.5 and 6.0 mg endrin/kg on the urinary excretion of the lipid metabolites formaldehyde, malondialdehyde, acetaldehyde and acetone. The simultaneous determination of these four lipid metabolites may be a useful biomarker for assessing exposure to xenobiotics which induce an oxidative stress and enhanced lipid peroxidation. Urine samples were collected up to 72 h post-treatment. The identities of the lipid metabolites were confirmed by gas chromatography-mass spectroscopy, while the 2,4-dinitrophenylhydrazine derivatives of these metabolic products were quantitated by high pressure liquid chromatography. Maximum increases in the excretion of the four lipid metabolites occurred at approx. 24 h post-treatment at all doses with no significant increases in excretion occurring thereafter. The maximum increases in excretion of malondialdehyde, formaldehyde, acetaldehyde and acetone were approx. 160%, 93%, 121% and 162%, respectively, relative to control values. Seventy-two hours after endrin administration, the liver weight/body weight and spleen weight/body weight ratios significantly increased while the thymus weight/body weight ratio markedly decreased. The results demonstrate that endrin induces dose- and time-dependent alterations in lipid metabolism with the enhanced excretion of specific metabolic products in the urine.

Biological monitoring of workers exposed to acetone in acetate fibre plants

Concentrations of acetone in urine, alveolar air, and blood were measured by gas chromatography with flame ionisation detection for 110 subjects occupationally exposed to acetone (mean 372 ppm) in three factories. Significant relations were found between the time weighted average environmental concentration and the concentration in the biological samples. The strongest correlation was between the concentration of acetone in urine and the degree of exposure (r = 0.71, 95% CI 0.64-0.77). This suggests that urinary acetone concentration is the best biological index of occupational exposure to acetone.

Curvi-linear relation between acetone in breathing zone air and acetone in urine among workers exposed to acetone vapor

An occupational health study was conducted on 45 acetone-exposed male workers in combination with 343 non-exposed men to examine the quantitative relationship between the intensity of acetone vapor exposure and the concentration of acetone in urine. The time-weighted average acetone concentrations were measured by means of diffusive samplers with water as absorbent, whereas urine samples were collected at the end of the shift as well as before the shift on the next morning. Acetone concentration in shift-end urine did not increase when the workers were exposed to acetone up to approx. 15 ppm, and this was followed by a gradual increase at a higher atmospheric acetone concentration, in a manner dependent to acetone vapor concentration. The comparison in acetone concentrations between the urine samples collected at the shift-end and those before the shift of the next morning showed that the levels in two sets of samples were the same among those exposed to 15 or less ppm acetone, whereas acetone in the shift-end samples was significantly higher than the counterpart levels in the pre-shift samples among those exposed to acetone at more than 15 ppm.

Excretion of formaldehyde, malondialdehyde, acetaldehyde and acetone in the urine of rats in response to 2,3,7,8-tetrachlorodibenzo-p-dioxin, paraquat, endrin and carbon tetrachloride

Formaldehyde (FA), acetaldehyde (ACT), malondialdehyde (MDA) and acetone (ACON) were simultaneously identified in urine, and their excretion quantitated in response to chemically induced oxidative stress. Urine samples of female Sprague-Dawley rats were collected over dry ice and derivatized with 2,4-dinitrophenylhydrazine. The hydrazones of the four lipid metabolic products were quantitated by high-performance liquid chromatography on a Waters 10-microns mu-Bondapak C18 column. The identities of FA, ACT, MDA and ACON in urine were confirmed by gas chromatography-mass spectrometry. An oxidative stress was induced by orally administering 100 micrograms/kg 2,3,7,8-tetrachlorodibenzo-p-dioxin, 75 mg/kg paraquat, 6 mg/kg endrin or 2.5 ml/kg carbon tetrachloride to rats. Urinary excretion of FA, ACT, MDA and ACON increased relative to control animals 24 h after treatment with all xenobiotics. The system has wide-spread applicability to the investigation of altered lipid metabolism in disease states and exposure to environmental pollutants.

[Determination of acetone, methanol, and methyl ethyl ketone in urine using head-space gas chromatography (HS.GC)]

Using HS.GC, We have succeeded in simultaneous determination of Ac, MeOH and MEK in urine without any complicated pretreatment or correction by internal standard. Moreover, in order to lower the detection limits of these materials, study was made on the salting out effect using 14 kinds of salts. As pretreatment, 2.0 ml of urine, 3.0 g of sodium sulfate and small sized magnetic stirrer are put into vial, which is sealed by septum. This is then heated for 10 min in warm bath of 50 degrees C. In order to dissolve the added salts as much as possible, the specimen is stirred by the stirrer. After cooling the liquid to room temperature, the specimen is analysed by HS.GC. The results showed that sodium sulfate was excellent synthetically. 1) Using the urine of workers not exposed to organic solvents three kinds of urine having specific gravity of 1.010, 1.024 and 1.034 were prepared and mixed standard organic solvents (Ac, MeOH and MEK) were added. Recovery percentages and coefficients of variation were calculated. The results showed that recovery percentages ranged from 92.0 to 101.7% and coefficients of variation from 0.2 to 4.6%. 2) The regression equations of standard curves were satisfactory with y = 9053x - 200(r = 0.999, n = 12) for Ac, y = 801x - 400 (r = 0.999, n = 12) for MeOH, and y = 15488x - 277 (r = 0.999, n = 12) for MEK. 3) The detection limits calculated by IUPAC formula were 0.0092 mg/l for Ac, 0.11 mg/l for MeOH and 0.0063 mg/l for MEK. These results indicated that this method is superior to other methods because the pretreatment is very simple, specificity is excellent, analysis by standard curves is possible, and this method is not affected by specific gravity of the urine.

High-performance liquid chromatographic determination of acetone in blood and urine in the clinical diagnostic laboratory

A method for the determination of acetone in plasma or urine by high-performance liquid chromatography (HPLC) was developed. Plasma specimens are deproteinized with acetonitrile (1:1, v/v) 2,4-dinitrophenylhydrazine (DNPH) is added to the supernatant or to filtered urine samples, similarly treated with acetonitrile (2:1, v/v) to prevent crystallization of the synthesized phenylhydrazone. An aliquot (20 microliters) of the reaction mixture was subjected to HPLC at ambient temperature using a reversed-phase Pecosphere 3 x 3 C18 column with acetonitrile-water (45:55, v/v) as eluent at a flow-rate of 1 ml/min and detection at 365 nm. Hydroxyacetone and acetoacetate phenylhydrazone derivatives do not interfere. The identification of acetone by its retention time was confirmed by comparison with a laboratory-synthesized acetone DNPH derivative. The concentration of acetone, eluted within 3 min, was determined by the peak-height method. The detection limit was 0.034 mmol/l; the relative standard deviations were less than 5% within run (n = 20) and less than 10% between run (n = 20).

A gas-chromatographic headspace method for the determination of acetone in bovine milk, blood and urine

An automated headspace gas-chromatographic method has been developed for the determination of acetone in the milk, blood and urine of dairy cows. Five ml samples were saturated with 2 g of sodium chloride and equilibrated for 30 min at 90 degrees C in a Hewlett-Packard HP 19395 A automatic headspace sampler. The headspace volatiles were transferred without splitting to a 25 m x 0.3 mm x 0.4 microns Carbowax column in a Shimadzu GC 9A gas chromatograph, operating isothermally at 50 degrees C. The coefficients of variation for the determination of acetone were 1.5-4.4% for urine, 10.0-24.9% for milk and 2.0-19.6% for blood. The detection limits were 0.0055 mg/100 ml for milk, 0.0072 mg/100 ml for blood and 0.0080 mg/100 ml for urine. The analysis time of 5 min per sample provided an adequate rate of throughput for routine monitoring.

Spectrophotometric determination of acetone using vanillin

A sensitive method is described for the spectrophotometric determination of acetone in water. Acetone reacts with vanillin in alkaline medium forming a yellow-orange dye with an absorption maximum at 430 nm. Beer's law is obeyed in the range from 0.5 to 5 p.p.m. of acetone in water. Molar absorptivity and Sandell's sensitivity were found to be 11.0 x 10(3) +/- 100 l mol-1 cm-1 and 0.005 micrograms cm-2, respectively. The important parameters for complete colour development were optimised and the method was used for the determination of acetone in biological samples. The method was also applied successfully to the determination of acetone in air after absorption in sodium hydrogen sulphite solution.

Biological monitoring of occupational exposure to isopropyl alcohol vapor by urinalysis for acetone

The relationship of the intensity of occupational vapor exposure to isopropyl alcohol (IPA) with urinary excretion of acetone and unmetabolized IPA was studied in 99 printers of both sexes, who were exposed to up to 66 ppm IPA (as time-weighted average), together with toluene, xylenes, methyl ethyl ketone and/or ethyl acetate. Acetone and IPA concentrations in urine were studied also in 34 non-exposed subjects. Acetone was detectable in the urine of most of the non-exposed, and the urinary acetone concentration increased in proportion to the IPA exposure intensity (r = 0.84 for observed, non-corrected values), whereas the correction for creatinine concentration or specific gravity of urine did not give a larger correlation coefficient. IPA itself was not found in the urine of the non-exposed, and was detectable in urine of only those who were exposed to IPA above a certain level, e.g. 5 ppm. The present study results suggest that urinary acetone is a valuable index for biological monitoring of occupational exposure to IPA as low as 70 ppm.

[Detection and determination of acetone using semiconductor sensors]

Investigations to examine not only the factors of influence on evaluation of acetone by self-prepared semiconductor gas sensors, but also to prove analytical properties, were carried out using different tools. A sensor temperature of 600 degrees C and a carrier gas flow-rate of 5 l/h were found to be suitable conditions for the measurement of flow-injection apparatus. The determination of 1 microliter-samples of aqueous solutions containing 1-700 g of acetone/l yielded deviations of 4 to 33%. Using a head space method, the working temperature of 370 degrees C led to a maximum sensor response, the detection limit ranged from 37.5 to 50 mg of acetone/l. After quantifying 5 microliters-sample solutions of 40-600 mg/l, results with an accuracy of 1 to 36% were obtained. The method showed the possibility of distinguishing concentrations of acetone below and above 40 mg/l according to physiological and pathological urinary values. The tests carried out on 100 human urine samples provide a good agreement with the Legal reference method for samples containing physiological or strong pathological amounts of ketone bodies, but not for those including traces and small amounts. False-positive results might be caused by a possible presence of ethanol in urine.

The generation of acetonemia/acetonuria following ingestion of a subtoxic dose of isopropyl alcohol

A subtoxic dose of isopropyl alcohol was ingested by three subjects to evaluate the time to and extent of acetone generation and to explore its detection in the urine. Maximal serum isopropyl alcohol concentrations were observed by 30 minutes after ingestion of approximately 1 oz 70% isopropyl alcohol (0.4 mL/kg), but maximal serum acetone concentrations were not recorded until at least four hours postingestion. Urine tested positive (small) for acetone within three hours of ingestion using Acetest urine testing tablets (Ames Labs, Elkhart, IN). It was concluded that acetonemia occurs early after ingestion of isopropyl alcohol and increases as serum isopropyl alcohol concentrations decline. In addition, acetonuria may be qualitatively measured by three hours postingestion with rapid urine screening tests and may remain positive for 24 hours.

[Use of gas chromatography with flame ionization (GC-FID) in the measurement of solvents in the urine]

The urinary concentration of some solvents (acetone, cyclohexane, 1,2 dichloropropane, n-hexane, methyl ethyl ketone, perchloroethylene, styrene, toluene, 1,1,1, trichloroethane) was measured by means of a gas chromatography Hewlett-Packard 5890 supplied with a flame ionization detector (GC-FID, DANI HS 3950). The coefficient of variation of the method was lower than 5%. The sensitivity of the GC-FID was very similar to what of mass spectrometer detector (GC-MSD, HP 5970 A).

1H NMR studies of urine during fasting: excretion of ketone bodies and acetylcarnitine

High-resolution 1H NMR spectroscopy has been applied to a study of urine from five normal human subjects during a 48-h period of fasting and for 22 h thereafter. The excretion rates of all three ketone bodies (acetoacetate, 3-D-hydroxybutyrate, and acetone), acetylcarnitine, creatinine, and sarcosine during this period were measured. Parallel increases in the excretion of the ketone bodies and acetylcarnitine were observed during fasting with little change in the output of creatinine and sarcosine.

Urinary elimination of acetone in experimental and occupational exposure

Fifteen volunteers were exposed to an acetone vapor concentration of 964-8, 610 mumol/m3 (56-500 mg/m3) for 2-4 h in an exposure chamber. Ten subjects were at rest during the exposure, and five were exposed at alternate rest and light physical exercise. Subsequently 104 workers occupationally exposed to acetone were studied. The relative uptake averaged about 53%, and the ratio of the alveolar concentration to the environmental concentration averaged about 0.28. Both for the experimentally exposed subjects and the occupationally exposed workers the urinary acetone concentration showed a linear relationship to the corresponding environmental time-weighted average concentration. A linear equation also existed between urinary concentrations and the amounts of acetone absorbed. The findings enable a consideration of the urinary concentration of the unaltered acetone as an appropriate exposure indicator and the proposal of a "biological equivalent threshold" to be used in the field of biological monitoring.

Ventricular tachycardia associated with non-freon aerosol propellants

A previously well 2-year-old child presented with seizures and ventricular tachycardia shortly after playing with an aerosol can of a well-known proprietary deodorant. She required intensive care and survived without sequelae. The propellants used in this product were isobutane, n-butane, and propane. The propellants have been thought to be safer than the previously used Freons, which were known to be cardiotoxic and neurotoxic. Significant exposure was confirmed by the detection of n-butane and isobutane in the patient's serum. We conclude that unintentional exposure to non-Freon aerosol propellants in a nonconfined space can be hazardous to children. Aerosol cans should be considered to represent toxic hazards and should be kept out of reach of children.

[Necessity for total trichloride compound measurement in screening tests for workers exposed to trichloroethylene or 1,1,1,-trichloroethane]

In 9 series of physical examinations legally required for trichloroethylene (TCE) workers, levels of urinary total trichloride compounds (TTC) were revealed to be generally high in 323 specimens, including 250 male ones, collected from a medium sized company. Sixty four specimens (19.8%), including 56 male ones (22.4%), exceeded 300 mg/l which are regarded to correspond to the threshold limit for TCE in the air of the work site. Four specimens had over 900 mg/l. In all 323 specimens, however, no abnormalities were found with respect to specific gravity of blood, hemoglobin concentration and urinary tests. TTC concentration values increased in specimens in the last 4 physical checkups, compared with the values measured in the first 5. The cause of this increase seemed to be related to increases in the number of products and the hours of overtime work. Symptoms felt by these workers gradually subsided as they were continuously exposed to TCE for more than 2 or 3 years. Some workers of long service had a tendency toward addiction to TCE. In the legally required environmental monitoring of TCE, and other harmful organic solvents, the 8 workplaces fell into either classification 1 or 2, indicating that the environmental conditions are not harmful. More importantly, the above evaluations did not take into account long hours of overtime put in by those workers. Turning to the checkups of 1,1,1-trichloroethane workers, the results of legally required physical checkups and environmental monitoring were almost the same as those for TCE.(ABSTRACT TRUNCATED AT 250 WORDS)

Toxicokinetics of [14C]hexafluoroacetone in the rat

The disposition and metabolism of [14C]hexafluoroacetone (HFA) were studied in the rat as part of an investigation of the mechanism of HFA-induced testicular atrophy. After sc injection of 13 mg/kg [14C]HFA, radioactivity was eliminated in a biphasic manner from the blood; the half-life of the initial phase was 22.6 hr and that of the elimination phase 75.1 hr. Following injection of 130 mg/kg [14C]HFA, the elimination of radioactivity was initially zero order, but with time it became first order and biphasic with half-lives of the initial and terminal elimination phases being 23.0 and 59.9 hr, respectively. The primary route of elimination was via the urine and all of the [14C]HFA was excreted unmetabolized. [14C]HFA was uniformly distributed throughout the major organs of the body with the exception of the liver which contained disproportionately higher levels of [14C]HFA. The hepatic binding of [14C]HFA was noncovalent and capacity limited. Notably, the testes, the target organ of HFA-induced toxicity, did not exhibit any unusual accumulation or retention of [14C]HFA.