Xenobiotics in food. I. Metabolic phthalate degradation

In conjunction with the programme of monitoring the food contamination by one of the most widely distributed contaminants--phthalic acid esters--the present investigation was focused on the elucidation of metabolic transformations of phthalates in the organism of the rat and humans and on assessment of the phthalate content of beef and pork liver. As a model substance di-(2-ethylhexyl)phthalate was selected. The paper contains new information on the mechanism of metabolic oxidative phthalate degradation in the rat, identifies the structure of intermediary products and suggests a reaction breakdown pattern. The balance of phthalate excretion from experimental animals in faeces and urine was examined, their metabolized ratio was defined and the phthalate load of the decisive parts of the organism was evaluated, i.e. in the liver, kidneys, spleen, brain and muscular tissue. Subsequent monitoring of phthalates in urine of human volunteers exposed only to the natural phthalate intake from contaminated food revealed the presence of some oxidative metabolites in body fluids. It provided also evidence of the possible endogenous formation of 2-ethyl-3-carboxypropylphthalic acid the presence of which may signalize metabolic oxidation by a pathway terminated by possible hepatocellular carcinogenicity of phthalates. The probability of introduction of oxidative phthalate metabolites from meat of domestic animals seems minimal.

Biotransformation of acrolein in rat: excretion of mercapturic acids after inhalation and intraperitoneal injection

Biotransformation of acrolein (ACR) was studied in vivo in the rat following inhalation and ip administration. The major and minor urinary metabolites were 3-hydroxypropylmercapturic acid (HPMA) and 2-carboxyethylmercapturic acid (CEMA), respectively. Male Wistar rats were exposed to ACR, 23, 42, 77 and 126 mg/m3, for 1 hr. The sum of mercapturic acids HPMA and CEMA excreted within 24 hr after the exposure amounted to 0.87 +/- 0.12, 1.34 +/- 0.5, 2.81 +/- 1.15, and 7.13 +/- 1.56 mumol/kg, i.e., 10.9 +/- 1.5, 13.3 +/- 5.0, 16.7 +/- 6.9, and 21.5 +/- 4.8% of the estimated absorbed dose, respectively. The dose estimate was based on reported values of minute respiratory volume and respiratory tract retention and was corrected for the ACR-induced changes in minute respiratory volume. In the relevant dose range (8.9 to 35.7 mumol/kg) the portion of mercapturic acids excreted was nearly constant for ip exposed rats. The sum of HPMA and CEMA amounted to 29.1 +/- 6.5% of the dose. These results indicate that the deficiency in rat lung metabolism of ACR to acrylic acid previously observed is not compensated by the other detoxication pathway in vivo, mercapturic acid formation. The health hazard arising from inhalation of ACR is likely to be higher than that from other routes of exposure.

Metabolic pathways of 1-butyl [3-13C]acrylate. Identification of urinary metabolites in rat using nuclear magnetic resonance and mass spectroscopy

1-Butylacrylate, an industrial monomer, is rapidly metabolized by carboxylesterase-catalyzed hydrolysis to acrylic acid and 1-butanol. Acrylic acid enters the intermediary metabolism and is efficiently degraded to carbon dioxide as the metabolic end product. To obtain a virtually complete metabolic pattern, rats were dosed by a single intraperitoneal dose of 1 mmol/kg 1-butyl [3-13C]acrylate. The urine was then analyzed by a one-dimensional 1H-detected and two-dimensional 1H-13C shift-correlated heteronuclear multiple-quantum NMR experiment. In this experiment, three urinary metabolites, namely, 3-hydroxypropanoic acid, N-acetyl-S-(2-carboxyethyl)cysteine, and N-acetyl-S-(2-carboxyethyl)cysteine sulfoxide, were identified comparing their 1H and 13C chemical shifts with those of authentic standards. In another experiment, to enhance minor metabolic pathways, rats were dosed with 0.25 mmol/kg of a carboxylesterase inhibitor, tri-o-tolyl phosphate, prior to 0.5 mmol/kg butyl [3-13C]acrylate. Under these conditions, N-acetyl-S-(2-carboxyethyl)cysteine, N-acetyl-S-[2-(butoxycarbonyl)-ethyl]cysteine, and N-acetyl-S-(2-carboxyethyl)cysteine sulfoxide were found in urine. No metabolites which would arise from a possible metabolic activation of 1-butyl acrylate to 1-butyl oxiranecarboxylate and its subsequent hydrolysis or glutathione conjugation were found. It is estimated that any metabolite amounting to more than 1% of the dose should be detected under these conditions. To study the routes by which BA enters the intermediary metabolism, incorporation of the label into urinary carboxylic acids was followed by GC/MS. Significant enrichment was found in 3-hydroxypropanoic acid and citric and isocitric acid but not in lactic acid.(ABSTRACT TRUNCATED AT 250 WORDS)

Biotransformation of diethenylbenzenes. IV. A simple high-performance liquid chromatographic method for separation of urinary metabolites of 1,3-diethenylbenzene on analytical and semi-preparative scales

A simple ion-suppression separation on reversed-phase columns, which is applicable for both analytical and semi-preparative work, is described. Six urinary metabolites of 1,3-diethenylbenzene (I), namely 1-(3-ethenylphenyl)-1,2-dihydroxyethane beta-D-glucosiduronates (two isomers, II and III), N-acetyl-S-[1-(3-ethenylphenyl)-2-hydroxyethyl]cysteine (IV), N-acetyl-S-[2-(3-ethenylphenyl)-2-hydroxyethyl]cysteine (V), 3-ethenylphenylmandelic acid (VI) and 3-ethenylphenylglyoxylic acid (VII), were isolated (Fig. 1). Four of them, IV-VII, have been identified in our previous work; the two glucosiduronates were identified for the first time by 1H NMR spectroscopy, fast atom bombardment mass spectrometry, and enzymic hydrolysis yielding 1-(3-ethenylphenyl)-1,2-dihydroxyethane as an aglycone. The method was reproducible the concentration range 0.05-5 mg/ml, the coefficient of variation being less than 7% (n = 5). Excretion of II-VI within 24 h in the urine of rats dosed with a single intraperitoneal injection of 100, 300 and 600 mg/kg I was determined quantitatively. The utility of the method is discussed in comparison with gas chromatographic-mass spectrometric techniques used previously.

Biotransformation of diethenylbenzenes. III: Identification of metabolites of 1,3-diethenylbenzene in rat

1. Biotransformation of 1,3-diethenylbenzene (1) in rat gave four major metabolites, namely, 3-ethenylphenylglyoxylic acid (2), 3-ethenylmandelic acid (3), N-acetyl-S-[2-(3-ethenylphenyl)-2-hydroxyethyl]-L-cysteine (4) and N-acetyl-S-[1-(3-ethenylphenyl)-2-hydroxyethyl]-L-cysteine (5) were isolated from urine and identified by n.m.r. and mass spectrometry. 2. Four minor metabolites, 3-ethenylbenzoic acid (6), 3-ethenylphenylacetic acid (7), 3-ethenylbenzoylglycine (8) and 2-(3-ethenylphenyl)ethanol (9) were identified by g.l.c.-mass spectrometric analysis of urine extract derivatized in two different ways. 3. All identified metabolites are derived from 3-ethenylphenyloxirane (10), a reactive metabolic intermediate. No product of any metabolic transformation of second ethenyl group has been identified. However, several minor unidentified metabolites were detected by g.l.c.-mass spectrometry. 4. Total thioether excretion in 24 h urine after a single i.p. dose of 1 amounted to 28.3 +/- 3.5 dose (mean +/- SD). No significant differences in the thioether fraction were observed in the dose range 100-300 mg/kg. 5. Thioether metabolites consisted mainly of mercapturic acids 4 and 5. The ratio of metabolites 5 to 4 was 62:38. Each mercapturic acid consisted of two diastereomers. Their ratio, as determined by quantitative 13C-n.m.r. measurement was 95:5 and 79:21 for mercapturic acids 4 and 5, respectively.