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1.
Analyst ; 120(4): 1091-6, 1995 Apr.
Article in English | MEDLINE | ID: mdl-7771674

ABSTRACT

Flow injection (FI), at a flow rate of microliter min-1, is an effective method for enzymic substrate determination using low concentrations of poly(ethylene glycol) (PEG)-stabilized soluble enzymes. PEG stabilizes dehydrogenase enzymes for at least several days by promoting sub-unit association. Band broadening of knitted open tubular reactors is reduced as flow rate decreases below 300 microliter min-1 and a small tubing diameter is important for a faster rate of absorbance signal increase with residence time. Small (0.5 microliter) sample injections also ensure narrow FI peaks. The determination of several substrates such as pyruvate, lactate, and cortisone using appropriate PEG-stabilized enzymes is demonstrated with this FI instrument at 25 or 50 microliters min-1 with sample throughputs of the order of 2-3 min per sample. The determination of lactate in serum samples is also possible. The advantage of this method, sample throughput, is not sacrificed but enzyme consumption is considerably less, compared to standard ml min-1 FI.


Subject(s)
Oxidoreductases , Animals , Flow Injection Analysis , Humans , Oxidoreductases/chemistry , Polyethylene Glycols/chemistry , Rabbits
2.
Int Arch Occup Environ Health ; 65(1 Suppl): S189-92, 1993.
Article in English | MEDLINE | ID: mdl-8406924

ABSTRACT

Predictions of human pesticide metabolism which are needed for the interpretation of biological monitoring data are frequently made from animal studies. Consequently, assumptions have to be made about the relationship between absorbed dose and metabolite excretion. The results from two human volunteer studies highlight the problems associated with extrapolating from animal studies in this way. The pyrethroid insecticide cypermethrin shows markedly different metabolite patterns when administered orally or dermally in man. Following dermal dosing the ratio of trans/cis cyclopropane acids is approximately 1:1, compared to 2:1 after oral administration. The ratio of total cyclopropane acids to phenoxybenzoic acids also differs depending on the route (dermal 1:4, oral 1:0.8). A knowledge of human metabolism by these two routes enables a much more meaningful interpretation of biological monitoring measurements. The herbicide molinate forms a mercapturate conjugate as a major urinary metabolite in the rat (35%). In volunteers at low dose levels this metabolite is present at insignificant levels (< 1%) and 4-hydroxymolinate is a much more abundant metabolite (39%). This shows that extrapolation between species can be very misleading. It is concluded that the benefits of using human volunteers for metabolism studies at low doses far outweigh the minimal risks involved. As a basis for biological monitoring such studies can lead to a greatly improved risk assessment for pesticides in use.


Subject(s)
Environmental Monitoring , Occupational Exposure/analysis , Pesticides/analysis , Thiocarbamates , Administration, Cutaneous , Administration, Oral , Azepines/administration & dosage , Azepines/analysis , Azepines/metabolism , Humans , Pesticides/metabolism , Pyrethrins/administration & dosage , Pyrethrins/analysis , Pyrethrins/metabolism , Risk
3.
Xenobiotica ; 22(8): 983-91, 1992 Aug.
Article in English | MEDLINE | ID: mdl-1413886

ABSTRACT

1. The pyrethroid insecticide cypermethrin was administered orally to six male volunteers as a single dose of 3.3 mg (cis: trans 1:1) and dermally to six volunteers at a dose of 31 mg/800 cm2 (cis:trans 56:44) as a soya oil-based formulation. Urine samples were collected for up to 5 days and analysed for the metabolites cis and trans 3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropane carboxylic acid (DCVA), 3-phenoxybenzoic acid (3PBA) and 3-(4'-hydroxyphenoxy) benzoic acid (4OH3PBA) following an acid hydrolysis procedure. 2. Following oral dosing approx. equal amounts of (cis+trans DCVA) and (3PBA+4OH3PBA) were excreted with peak excretion rates occurring between 8 and 24 h after dosing. The ratio of trans:cis DCVA was on average 2:1. Based on DCVA measurements the amount of cypermethrin absorbed was estimated to be between 27% and 57% (mean 36%) of the administered dose. 3. Peak urinary excretion rates of metabolites occurred between 12 and 36 h after dermal dosing. The amount of metabolites derived from the phenoxybenzyl moiety (3PBA+4OH3PBA) was on average 4 times greater than the amount of (cis+trans DCVA) recovered in urine. The ratio of trans:cis DCVA was, on average 1:1.2. Based on the recovery of the phenoxybenzyl metabolites it is estimated that 0.85-1.8% (mean 1.2%) of the administered cypermethrin was absorbed. 4. These studies demonstrate marked differences in the urinary metabolite profile by the two routes, and provide an improved basis for determining the extent and main route of absorption of cypermethrin under occupational exposure conditions.


Subject(s)
Insecticides/metabolism , Pyrethrins/metabolism , Administration, Cutaneous , Administration, Oral , Adult , Humans , Insecticides/administration & dosage , Male , Pyrethrins/administration & dosage
4.
Int Arch Occup Environ Health ; 64(5): 383-7, 1992.
Article in English | MEDLINE | ID: mdl-1487335

ABSTRACT

Two groups of three male volunteers were exposed to atmospheric concentrations of either 327 or 1833 mg m-3 chlorodifluoromethane (HCFC22) for 4 h. Blood, urine and expired air samples were taken during and after the exposure period and analysed for HCFC22. Urine samples were also analysed for fluoride ion. During the exposure period, blood concentrations of HCFC22 approached a plateau, and the average peak blood concentrations of 0.25 and 1.36 micrograms cm-3 were proportional to dose. HCFC22 concentrations in expired air were similar to the exposure concentration during the exposure period. The ratio between venous blood and breath concentrations of HCFC22 towards the end of the exposure period was on average 0.77, which is consistent with in vitro estimates of the partition coefficient. In the post-exposure period, three phases for the elimination of HCFC22 were identified, with estimated half-lives of 0.005, 0.2 and 2.6h. HCFC22 was detected in urine samples taken in the post-exposure period, and the rate of decline was consistent with the terminal rate of elimination estimated from blood and breath measurements. On average 2.1% of the inhaled HCFC22 was recovered in breath within 26 h of exposure. This is consistent with the low solubility in blood and fat. Minimal changes in fluoride ion concentrations in urine following exposure indicate that HCFC22 is unlikely to be metabolised to a significant extent. Following inhalational exposure HCFC22 is poorly absorbed and is rapidly eliminated from the body. Possible biological monitoring strategies could be based on measurements of HCFC22 in urine or breath samples collected after the end of an exposure period.


Subject(s)
Air Pollutants, Occupational/pharmacokinetics , Chlorofluorocarbons, Methane/pharmacokinetics , Occupational Exposure , Adult , Half-Life , Humans , Male , Maximum Allowable Concentration , Metabolic Clearance Rate
5.
Int Arch Occup Environ Health ; 62(1): 73-8, 1990.
Article in English | MEDLINE | ID: mdl-2295526

ABSTRACT

Seven male volunteers were exposed to atmospheric concentrations of either 1980, 4100 or 7630 mg m-3 1,1,2-trichloro-1,2,2-trifluoroethane (FC113) for 4 h. Blood and expired air samples were collected during the exposure period and for several days subsequently and analysed for FC113. Blood and breath concentrations of FC113 were related to the administered dose with some variation between individuals. The low blood/breath ratios measured are consistent with the low solubility of FC113 in blood. The absorption and elimination of FC113 can be described by a three-compartment model and the average half-lives of elimination of FC113 in breath were 0.22, 2.3 and 29 h. A pulmonary retention during the exposure period of 14% was measured but only 2.6 to 4.3% of the dose was recovered unchanged in breath after the exposure period, suggesting that FC113 could be metabolised following inhalation exposure. It is concluded that a practical method for biological monitoring during occupational exposure would be to measure end-tidal breath concentrations of FC113 in samples taken the morning after exposure. The predictive value of such a measurement can be improved if the results are normalised to the body fat content of individual workers which can be estimated from height and weight measurements.


Subject(s)
Chlorofluorocarbons, Methane/pharmacokinetics , Administration, Inhalation , Air Pollutants, Occupational/analysis , Breath Tests , Chlorofluorocarbons, Ethane , Humans , Male
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