. Urinary excretion of hippuric acid and m-or p-methylhippuric acid in the urine of persons exposed to vapours of toluene and m-or p-xylene as a test of exposure. Twenty-three male volunteers were exposed in groups of four or five to toluene and m-and p-xylene vapour for periods of 3 hours or of 7 hours with one break of an hour. Urine was collected at hourly intervals for several hours, and thereafter all urine was collected until 18 hours after the end of the exposure period, and was analysed for hippuric and methylhippuric acids. It was shown that hippuric acid was excreted equivalent to 68 % of the toluene absorbed, and m-methylhippuric acid equivalent to 72% of the m-xylene absorbed. Up to hydrocarbon concentrations of 200 ppm the total quantity of hippuric acids excreted was proportional to the total exposure (ppm x hours). In descending order of precision the following were also related to exposure: rate of excretion during the exposure period; concentrations of hippuric acid in urine corrected to constant urine density; and concentrations in urine uncorrected for density. The last could not be used to calculate exposure, but the others could be to give screening tests to show whether workmen could have been exposed to concentrations greater than the maximum allowable.The effects of exposure on blood pressure, pulse rate, flicker value, and reaction time were measured. There were some variations which suggested that the MAC of toluene should be set higher than 200 ppm.For the reasons given by Ogata, Tomokuni, and Takatsuka (1969), exposure to toluene and m-or p-xylene is best estimated by determining the quantities of their metabolites, hippuric acid and m-or p-methylhippuric acid, excreted in the urine. Using the analytical methods already described (Ogata et al., 1969) we show here how the quantities of metabolites are related to exposure, and consequently what levels of metabolites in urine cor-
Commercial heterogeneous solvent products (e.g., paints, inks and adhesives) were collected nationwide in Japan in 1980. The vapor phase of the product containers were analyzed for volatile organic solvent constituents by means of FID-gas chromatography on two FS-WCOT (OV-101 and PEG-600) capillary columns. Of 657 products collected (358 paints, 62 inks, 165 abhesives and 72 others), 136 samples were not analyzable because 75 gave numerous peaks (presumably containing gasoline) and others had no volatile component. Among the remaining 521 samples (298 paints, 52 inks, 120 achesives and 51 others), 70 gave only one peak while others gave multiple peaks, indicating the mixture of solvents rather than single solvent was commonly used. Of the organic solvent components identified, toluene was the most popular solvent throughout paints
The abnormalities in acatalasemia at the gene level as well as properties of the residual catalase in Japanese acatalasemia are historically reviewed. The replacement of the fifth nucleic acid, guanine, in the fourth intron by adenine in the acatalasemic gene causes a splicing mutation and hence a deficiency of mRNA. The guanine-to-adenine substitution was detected in two Japanese acatalasemic cases from different families. The properties of the residual catalase are similar to those of normal catalase; the exons are identical. The properties of the residual catalase and the molecular defect in the catalase gene are compared among Japanese, Swiss, and mouse acatalasemias. The physiological role of catalase, as judged from human acatalasemic blood and acatalasemic mice, is also described.
A simple method for the determination of 4-chlorocatechol (ClCh, 4-chloro-1,2-benzenediol) and chlorophenols (ClPh), metabolites of monochlorobenzene (ClBz), in urine by high performance liquid chromatography (HPLC) is described. Enzymatic hydrolysates of urine were applied to a stainless-steel column packed with octadecyl-silanized silica gel, and a mixed solution of 20 mM potassium phosphate monobasic: acetonitryl (75:25, v/v) was used as a mobile phase. The procedures for ether extraction and evaporation of extract could be omitted. The accuracy and precision of the present HPLC method were satisfactory. The excretion kinetics of ClCh and p-ClPh were investigated over 35 h after cessation of ClBz inhalation. Proportional relationships between concentrations of ClBz in air and of its metabolites in urine were observed. The slopes of regression lines predicting the levels of ClCh, p-ClPh and total ClPh in urine taken during the last 2 h of exposure to ClBz in air were 6.56, 1.13 and 2.83 mg/g creatinine for 1 ppm ClBz, respectively. ClBz in the blood and the end exhaled air of subjects at the end of exposure were identified by gas chromatography (GC) and mass spectrometry. A proportional relationship was observed between the concentration of ClBz in air and that in blood. The validity of the threshold limit value (TLV) for ClBz as evaluated from the subjective and objective symptoms is discussed.
An automated high performance liquid chromatographic method (HPLC) for the direct determination of urinary concentrations of hippuric acid (HA), and o-, m- and p-methyl hippuric acids (MHAs), metabolites of toluene and o-, m-, and p-xylenes, and of urinary phenyl glyoxylic acid (PGA) and mandelic acid (MA), metabolites of styrene or ethylbenzene, is described. Methanol was added to urine, the mixture was centrifuged and the supernatant was injected into HPLC. A stainless-steel column packed with octadecyl silanized silicate was used and the mobile phase was a mixed solution of 5 mM potassium phosphate monobasic/acetonitrile (90/10). The method is simple and specific. Urine can be analyzed without solvent extraction. Analysis can be performed satisfactorily within 45 min for samples containing HA, MHAs, PGA and MA, and within 15 min for those containing HA, PGA and MA. Another automated HPLC method for the determination of urinary concentrations of phenylsulfate (PhS) and phenylglucuronide (PhG), metabolites of benzene and phenol, is also described. Urine was centrifuged and the supernatant was injected into HPLC. A column packed with octadecyl silicate and a mobile phase of 50 mM of potassium phosphate monobasic/acetonitrile (85/15) were used. The whole analyses and quantitative determination can be performed within 15 min for samples containing PhS and PhG in the worker's urine with a simple mobile phase. The accuracy and precision in the present methods by the use of automated HPLC were satisfactory.
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