Gene/Protein Disease Symptom Drug Enzyme Compound
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Query: EC:3.2.1.31 (beta-glucuronidase)
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A liquid chromatographic (LC) method was developed for the determination of flunixin (FNX) in raw bovine milk. The milk was acidified and mixed with silica gel, and the mixture was packed into a chromatographic column. The column was defatted with water-saturated dichloromethane-hexane (30 + 70, v/v), and the analyte was eluted with EtOAc. The EtOAc extract was washed with water at pH 3.5, the water was discarded, and the EtOAc layer was then extracted with 0.1M NaOH. The aqueous layer was drained, passed through a primed C18 solid-phase extraction (SPE) column, and eluted with EtOAc. The EtOAc layer was dried under N2, taken up in a solution of MeOH-(5 mM tetrabutylammonium [TBA]-H2PO4 + 2 mM NaOH) (50 + 50), sonicated, and filtered. FNX was determined by LC using a C18 column (ODS Hypersil), a mobile phase mixture of 58% A (MeOH) and 42% B (5 mM TBA-H2PO4 + 2 mM NaOH), and a diode-array ultraviolet detector at 285 nm. FNX was determined in raw milk at 5 spiking levels (5, 10, 20, 40, and 80 ng drug/mL milk). Absolute recoveries ranged from 69.6 to 74.4%, and relative standard deviations ranged from 1.1 to 6.9%. The limit of quantitation was 1.7 ng drug/mL milk. A lactating cow was dosed intravenously (2.2 mg/kg) with flunixin meglumine (Banamine) to generate incurred milk residues. FNX residues ranged from 7.34 ng/mL at 16 h postdose to 1.74 ng/mL at 24 h postdose. Both levels were obtained with additional beta-glucuronidase treatment (almost no incurred drug was detected at these low levels without the enzyme treatment).(ABSTRACT TRUNCATED AT 250 WORDS)
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PMID:Determination of flunixin in milk by liquid chromatography with confirmation by gas chromatography/mass spectrometry and selected ion monitoring. 758 Mar 36

Sensitive and selective high performance liquid chromatographic (HPLC) methods for the quantification of 1,2-diethyl-3-hydroxypyridin-4-one (CP94), its iron complex [Fe(III) (CP94)3] and glucuronide metabolite (CP94-GLUC) in urine and serum of thalassaemic patients are described. Three separate analyses are involved. The first assay quantifies both CP94 and its iron complex. This procedure requires the conversion of the iron complex to the free ligand and is carried out using diethylenetriaminepentaacetic acid (DTPA). CP94 and the internal standard, 1-propyl-2-ethyl-3-hydroxypyridin-4-one (CP95) present in either serum or urine are then extracted at pH 7.0 with dichloromethane. Extraction efficiency is 96.0 +/- 5.6% and 100 +/- 7.1% for CP94 and CP95, respectively, and 31.2 +/- 2.1% at 30 microM and 53.2 +/- 4.2% at 300 microM for the corresponding iron complex. In the second assay, samples are incubated (16 h) with beta-glucuronidase and processed as before. In this assay, the drug, its iron complex and glucuronide conjugate are measured. In the third assay the iron complex of CP94, [Fe(III) (CP94)3] is quantified. From the three separate analyses it is possible to calculate the individual concentrations of the three separate components present in serum and urine of thalassaemic patients. Calibration for both components, i.e. CP94 (assays 1 and 2) and its iron complex (assay 3) are linear with correlation coefficients > 0.99 and are reproducible over the required concentration range of 0-500 microM for the free ligand and 0-100 microM for the iron complex. The minimum quantifiable level is 0.5 microM for the free ligand and 1.0 microM for the iron complex.
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PMID:HPLC determination of 1,2-diethyl-3-hydroxypyridin-4-one (CP94), its iron complex [Fe(III) (CP94)3] and glucuronide conjugate [CP94-GLUC] in serum and urine of thalassaemic patients. 798 22

An HPLC method for the determination of dextrorphan, an active metabolite of dextromethorphan, in plasma was established using column switching technique. The column switching system was equipped with a per-column of 30 mm x 5 mm ID, packed with mu Bondapak C18, 37-50 microns, and an analytical column of 150 mm x 5 mm ID, packed with YWG-C18, 5 microns. A 0.2% acetic acid solution was used as the pretreating mobile phase to wash out impurities from the per-column. The analytical mobile phase consisted of acetonitrile-water-acetic acid-triethylamine-dichloromethane (17:82:1:0.05:0.025). The plasma samples were directly injected into the HPLC system after enzymatic hydrolysis of dextrorphan glucuronide ester conjugate to free form with beta-glucuronidase. The dextrorphan was monitored with a fluorescence detector at 290 nm (excitation) and 315 nm (emission). The method was linear within the plasma concentration range of 20-640 ng/ml (r = 0.9987), and the detection limit was 4 ng/ml. The mean recoveries of the method averaged 103.8%. The relative standard deviations of the assay were less than 10% for both within-day and between-days.
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PMID:[Column switching HPLC method for determination of dextrorphan, an active metabolite of dextromethorphan, in plasma]. 823 84

Consumption of fossil fuels has increased indoor and outdoor concentrations of polycyclic aromatic hydrocarbons (PAHs) and nitrogen dioxide (NO2). To study the combined effect of PAH administration and NO2 exposure on mutagenicity of urine from animals we injected 400 mg/kg body wt i.p. one of five kinds of PAH (pyrene, fluoranthene, fluorene, anthracene and chrysene) into ICR mice, Wistar rats, Syrian golden hamsters or Hartley guinea pigs after exposure to 20 p.p.m. NO2 gas for 24 h and then exposed the animals to NO2 gas for an additional 24 h. During the latter 24 h we collected the urine and assayed its mutagenicity with the Ames Salmonella strains after treatment with beta-glucuronidase and arylsulfatase and extraction with dichloromethane. The urine from mice treated with both PAH and NO2 showed high mutagenicity for Salmonella typhimurium strains TA98 and TA100, whereas the urine from mice treated with PAH and air showed almost no mutagenic activity. The mutagenicity was decreased in nitroreductase- and acetyltransferase-deficient strains TA98NR and TA98/1,8-DNP6 respectively. Treatment with a mixture of 20% of each of the five kinds of PAH and NO2 augmented the urinary mutagenicity of mice 1.5-fold. The urine from hamsters treated with pyrene or fluoranthene and NO2 was also highly mutagenic, but that from rats or guinea pigs was not very mutagenic. The mutagenicity was also decreased in strains TA98NR and TA98/1,8-DNP6. These results suggest that the urine contains nitro compounds and that the nitration of PAHs occurs in the body of animals under exposure to NO2 gas. Actually, the nitrated metabolites of pyrene, 1-nitro-6/8-hydroxypyrene and 1-nitro-3-hydroxypyrene, were detected in the urine from mice treated with pyrene under exposure to NO2 gas. To elucidate the mechanism of in vivo nitration, NO2 (20 p.p.m.) was bubbled through 50 mM Tris-HCl buffer (pH 7.4) or dichloromethane solution containing pyrene or 1-hydroxypyrene (10 microg/ml). Pyrene was not nitrated by NO2 in either aqueous or organic solutions. However, 1-hydroxypyrene was changed to nitrohydroxypyrenes by NO2 in the Tris-HCl buffer, but not in the organic solution. Ascorbic acid, alpha-tocopherol, glutathione oleic acid and hemoglobin were found to inhibit the nitration of 1-hydroxypyrene in aqueous solution. The urinary mutagenicity of mice treated with both pyrene and NO2 was also decreased by oral administration of ascorbic acid and alpha-tocopherol. These results suggest that 1-hydroxypyrene is nitrated by an ionic reaction in the animal body after hydroxylation of pyrene in the liver.
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PMID:In vivo formation of mutagens by intraperitoneal administration of polycyclic aromatic hydrocarbons in animals during exposure to nitrogen dioxide. 870 53

We developed a high-performance liquid chromatography (HPLC) method for quantitating p-hydroxy-N-benzylamphetamine glucuronide (pHBAG) and p-hydroxy-benzphetamine glucuronide (pHBZG), which are urinary metabolites of benzphetamine, in humans. Urine samples were hydrolysed with beta-glucuronidase (EC 3.2.1.31) at 37 degrees C overnight and the treated urine was applied to a solid phase extraction column. After washing the column with water, 0.01 mol/L acetic acid and methanol, pHBA and pHBZ were eluted with dichloromethane:isopropanol:28% ammonium hydroxide (78.4:19.6:2.0 v/v). The eluate was evaporated and the residue was dissolved in acetonitrile: 5 mmol/L 1-pentane sulphonic acid (5:95 v/v) and analysed by HPLC with gradient elution. The amounts of urinary pHBAG and pHBZG excreted by two human subjects after oral administration of 10 mg benzphetamine hydrochloride were determined. About 10-15% of benzphetamine was found to be excreted as pHBAG and pHBZG, and almost all of these metabolites were excreted within 24 h. Urine samples should be collected as early as possible after ingestion of benzphetamine to detect pHBAG and pHBZG.
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PMID:Development of a method for the quantitation of benzphetamine metabolites in human urine by high-performance liquid chromatography. 983 92

We developed a method for simultaneous analysis of benzphetamine (BZ) and its metabolites, p-hydroxy-N-benzylamphetamine (pHBA), p-hydroxybenzphetamine (pHBZ), amphetamine (AP), methamphetamine and p-hydroxymethamphetamine by micellar electrokinetic chromatography (MEKC). Urine samples from 0-15 h (3-h intervals) after oral administration of BZ (10 mg) were hydrolyzed with beta-glucuronidase (EC 3.2.1.31) at 37 degrees C overnight. The treated urine was applied to a solid phase extraction column Bond Elut Certify. After sequentially washing the column with water, 0.1 mol/l acetic acid and methanol, the samples were eluted with dichloromethane:isopropanol:28% ammonium hydroxide=78.4:19.6:2.0 (v/v %). The eluate was evaporated and the residue dissolved in running buffer was analyzed by MEKC. In urine from 0-3 h, AP, pHBZ and pHBA were detected. After that, only pHBA, which is one of the major metabolites of BZ in human urine, could be detected in the urine by the present method. A method for quantitation of pHBA by MEKC is described here. The effects of acetonitrile and sodium dodecyl sulfate in the running buffer of MEKC on the separation of BZ and its metabolites are also reported.
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PMID:Simultaneous analysis of benzphetamine and its metabolites, and quantitation of urinary p-hydroxy-N-benzylamphetamine by micellar electrokinetic chromatography. 985 14

trans-3'-Hydroxycotinine (THOC) has been recognized as the most abundant metabolite of nicotine. In an attempt to assess THOC and cotinine (COT) concentrations during nicotine transdermal therapy, we developed a new quantitative gas chromatography-mass spectrometry (GC-MS) method for simultaneous determination of total and free THOC and COT in human urine. The method utilizes the following: (a) hydrolysis of conjugated THOC and COT by beta-glucuronidase; (b) basic extraction of THOC and COT with mixed dichloromethane and n-butyl acetate; (c) derivatization of THOC with bis(trimethylflurosilyl)acetamide; and (d) separation and identification by GC-MS with selective ion monitoring. Lower limits of quantification for the assay were 50 and 20 microg/L for THOC and COT, respectively. The intra- and interassay CVs were 4.4% and 11% for THOC, and 3.9% and 10% for COT at 1000 microg/L. The results from six consecutive 24-h urine collections in 71 subjects administered daily transdermal nicotine doses of 11, 22, and 44 mg showed that, on average, free THOC was 76% of total THOC and free COT was 48% of total COT in all subjects. THOC is the major metabolite of nicotine and constitutes 20% of total nicotine intake at steady state, whereas urinary nicotine and COT excretion were 8% and 17%, respectively. The method is useful for simultaneous determination of free and total THOCand COT and can be used to assess the urinary excretion of these metabolites during transdermal nicotine therapy.
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PMID:A new gas chromatography-mass spectrometry method for simultaneous determination of total and free trans-3'-hydroxycotinine and cotinine in the urine of subjects receiving transdermal nicotine. 989 42

Liquid-liquid (using dichloromethane) and liquid-solid extraction processes (using disposable C18 cartridges) were applied to human urine samples spiked with 15 androgenic anabolic steroids (natural and synthetic). The extraction recoveries were assessed from different HPLC separations of anabolic steroids using water-acetonitrile mobile phase, and using calibration graphs obtained by injection into HPLC of standard samples of these compounds before and after extraction. The procedures, including sample preconcentration, showed extraction efficiencies over 90% which were independent on a wide range of concentrations tested. Solid phase extraction yielded poor results for oximetolone, danazol and dehydroepiandrosterone. For real urine samples, hydrolysis using beta-glucuronidase and washing using sodium hydroxide before and after solvent extraction, respectively, is recommended.
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PMID:Solvent and solid-phase extraction of natural and synthetic anabolic steroids in human urine. 1133 85

Penicillium canescens oxidises dibenzofuran (DBF) to produce monohydroxylated derivatives and other more hydrophilic metabolites. These substances are water-soluble but unstable in organic solvents such as ethyl acetate, acetone or dichloromethane. Both extraction with ethyl acetate and enzymatic treatment of the aqueous culture filtrate with beta-glucuronidase led to decay of the hydrophilic metabolites and indicated these products to be glycoside conjugates. The glycosyl residue was identified as glucose both by liquid chromatography and by the use of glucose oxidase. The conjugate pattern formed was the same in type and amount, independent of the carbon source used for cultivation of the fungus. Clearly, DBF transformation in P canescens occurred in two phases: first the conversion to 2-, 3-, and 4-hydroxydibenzofuran (phase I), followed by the formation of the corresponding glucosyl conjugates (phase II). In contrast, 2,3-dihydroxydibenzofuran added to the cultures was transformed by ring cleavage producing a muconic acid-like dead-end product.
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PMID:Formation of glucoside conjugates during biotransformation of dibenzofuran by Penicillium canescens SBUG-M 1139. 1175 91

A method of analysis was developed to determine free and glucuronated monobutyl phthalate (BuP) and monobenzyl phthalate (BeP) in urine for the assessment of exposure of man to butylbenzyl phthalate (BBP) in the workplace and in the environment. This method has also been applied in pharmacokinetic studies in experimental animals and the determination in urine of exposed workers. Urine samples are first subjected to enzymatic hydrolysis with beta-glucuronidase to enable the measurement of the total amount of monophthalates excreted. A fraction of the hydrolysate is used for further analysis. Monohexyl phthalate is added as an internal standard and the hydrolysed urine extracted with a n-hexane/dichloromethane mixture after acidification and saturation with salt. The organic fractions are washed, dehydrated and evaporated. The residue is methylated by means of diazomethane dissolved in diethylether, evaporated and further purified by extraction into n-hexane from an alkaline buffer. The organic fractions are evaporated and the residue redissolved in acetonitrile for analysis by ion trap GC-MS equipped with a 50 m apolar WCOT capillary column. TIC mass chromatograms are recorded from which SIM chromatograms can be derived electronically. The m/z values used are 91, 149, and 163 which provide a sufficient sensitive response and which are specific enough to pick up the methylated monophthalates under investigation. The quantitative limit of detection (LOQ) is 60 micrograms/L for BuP and BeP when using the Magnum ion Trap detector and 3 micrograms/L when using the Polaris Q in the splitless mode. The calibration curve in urine is linear from 120 micrograms/L to 50,000 micrograms/L with a coefficient of variation of less than 10%. In case of the Polaris Q linearity started from 10 micrograms/L. The recovery of the method is monitored by the response signal of the internal standard in the ion chromatogram. In the event of insufficient recovery the analysis is repeated. Variations in recovery are compensated by the internal standard of which the molecular structure is very similar to the ones of the monophthalates under investigation.
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PMID:[Determination of monoester metabolites of butylbenzyl phthalate (BBP) by GC-MS in the urine of exposed workers]. 1197 37


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