Želimira Vasilić

Urinary excretion of diethylphosphorus metabolites in persons poisoned by quinalphos or chlorpyrifos

The urinary excretion rates of diethyl phosphate and diethyl phosphorothioate and changes in blood cholinesterase activities were studied in fifteen persons self-poisoned either by the organophosphorus pesticide quinalphos (twelve persons) or by chlorpyrifos (three persons). The organophosphate poisoning was always indicated by a significant depression of serum and/or red blood cell cholinesterase activities. The return of serum cholinesterase activity in the range of referent values took more than 30 days and had a different course in different persons. The most rapid increase in red blood cell acetylcholinesterase activity was noted within 24 h after the first treatment with oximes Pralidoxime and/or HI-6. None of the spot urine samples, collected daily after admission of persons to hospital, contained measurable quantities of the parent pesticide. There was no correlation between the maximum concentration of total urinary diethylphosphorus metabolites normalized to creatinine and the initial inhibition of blood cholinesterase activities measured in samples collected on the day of admission to hospital. The excretion of metabolites followed the kinetics of a biphasic reaction. The half-time of urinary metabolites concentration decrease in the fast excretion phase in quinalphos poisoned persons was 5.5–14.2 h (eight persons) and 26.8–53.6 h (four persons) and in chlorpyrifos poisoned persons 3.5–5.5 h. The half-time for the slow excretion phase ranged from 66.5 to 127.9 h in all persons and for both compounds. For a given person, the rates of excretion of diethyl phosphate and diethyl phosphorothioate were about the same. However, in quinalphos poisoned persons the proportions of single metabolites in total diethylphosphorus metabolites varied with the initial maximum concentration of total metabolites. Simultaneous determination of both metabolites gave a more reliable and sensitive confirmation of absorption and retention of quinalphos and chlorpyrifos in the body.

Chlorpyrifos metabolites in serum and urine of poisoned persons

Concentrations of parent pesticide and corresponding diethylphosphorus metabolites in blood serum and urine were investigated in persons who had ingested a concentrated solution of organophosphorus pesticide chlorpyrifos. The organophosphate poisoning was indicated by a significant depression of blood cholinesterase (EC 3.1.1.7 and EC 3.1.1.8) activities. Blood and spot urine samples were collected daily after admission of the persons to hospital. Chlorpyrifos was detected only in serum samples in a period up to 15 days after poisoning. In the same samples chlorpyrifos oxygen analogue, chlorpyrifos oxon, was not detected. The presence of diethylphosphorothioate in all serum and urine samples confirmed that part of chlorpyrifos was hydrolysed before its oxidation. The maximum concentrations of chlorpyrifos in serum and of metabolites in serum and urine were measured on the day of admission. The decrease in concentrations followed the first-order kinetics with the initial rate constant faster and the later one slower. In the faster elimination phase chlorpyrifos was eliminated from serum twice as fast (t1/2 = 1.1-3.3 h) as the total diethylphosphorus metabolites (t1/2 = 2.2-5.5 h). The total urinary diethylphosphorus metabolites in six chlorpyrifos poisoned persons were excreted with an average elimination half-time of 6.10 +/- 2.25 h (mean +/- S.D.) in the faster and of 80.35 +/- 25.8 h in the slower elimination phase.

Dialkylphosphorus metabolites in the urine and activities of esterases in the serum as biochemical indices for human absorption of organophosphorus pesticides

Ninety-seven agricultural workers were monitored for absorption of the organophosphorus pesticides methidathion, vamidothion, and azinphos-methyl, which were sprayed in an orchard during two seasons. Low levels of only one dialkylphosphorus metabolite (dimethyl phosphorothioate) were found in only eight workers in pre-exposure urine samples. More than one dialkylphosphorus metabolite was detected in almost all exposed individuals in after-exposure urine samples. The highest concentrations were measured after exposure to azinphos-methyl; the median concentrations of dimethyl phosphorodithioate and dimethyl phosphorothioate were 0.92 and 0.78 nmol/mg creatinine with a concentration range up to 14.3 and 53.7, respectively. Three diethylphosphorus metabolites were also detected in some samples, but at lower concentrations. Cholinesterase activities were decreased (31–48%) in the serum of 12 workers; four of those workers had no dialkylphosphorus metabolites in the urine. Paraoxonase and arylesterase activities in the serum were unaffected by the absorption of pesticides, and there was no correlation between the activities of these esterases and the metabolite concentrations in the urine. This study confirmed that dialkylphosphorus metabolites in the urine are a more sensitive index of absorption than cholinesterase inhibition in the serum but lack of correlation between cholinesterase inhibition and metabolite concentration indicates that both parameters should be monitored.

DIMETHYLPHOSPHORUS METABOLITES IN SERUM AND URINE OF PERSONS POISONED BY MALATHION OR THIOMETON

The urinary excretion rates of dimethyl-phosphate, -phosphorothioate and -phosphorodithioate were studied in six persons of whom four had ingested a concentrated solution of malathion and two of thiometon. The concentration decrease of single and total dimethylphosphorus metabolites was biphased, with a fast initial rate and a slow later rate. The excretion rate of total metabolites in the faster phase depended on the initial concentration in urine. At concentrations higher than 100 nmol/mg creatinine, the excretion half-times ranged from 7.5 to 15.4 h and at concentrations between 52 and 95 nmol/mg creatinine from 34.7 to 55.4 h. Non-metabolized malathion was detected only in one urine sample collected from one person immediately after hospitalization. Two persons poisoned with malathion were taken blood serum samples for the analysis of the parent pesticide and its metabolites on a daily basis after hospitalization. The parent pesticide was detectable in the serum only one day after the poisoning. The concentration of total malathion dimethylphosphorus metabolites in serum decreased very quickly within 1.5 days after hospitalization. The total metabolite elimination half-times were 4.1 and 4.7 h in the initial phase, and 53.3 and 69.3 days in the later slower elimination phase. There was no correlation between maximum concentrations of total metabolites measured in serum and/or urine on the day of admission to hospital and the initial depression of serum cholinesterase (BChE, EC 3.1.1.8) and erythrocyte acetylcholinesterase (AChE, EC 3.1.1.7).

Diethylphosphorus metabolites in serum and urine of persons poisoned by phosalone

The presence and elimination rate of phosalone and its diethylphosphorus metabolites in blood serum and urine were studied in persons who had ingested a concentrated phosalone solution. Phosalone was detected only in serum samples. As it was rapidly hydrolysed and eliminated from the body, its diethylphosphorus metabolites were a more sensitive indicator of exposure. The concentration decrease of phosalone in serum and of total diethylphosphorus metabolites in serum and urine followed the kinetics of a biphasic reaction. The faster elimination half-times in serum, calculated for two persons, were 2.3 and 3.4 h for phosalone and 3.4 and 38.6 h for total diethylphosphorus metabolites. In the faster phase the average elimination half-time of total urinary metabolites in five persons was 25 +/- 17 h. The kinetic data for total urinary metabolites in a person occupationally exposed to phosalone indicated an early and very fast elimination phase (elimination half-time 1.3 h), which was overlooked in poisoned persons. The proportions of single metabolites in total urinary metabolites in poisoned persons depended on whether the total amount of diethylphosphorus metabolites was above 1000 or below 1000 nmol/mg creatinine. Diethylphosphorodithioate predominated at high and diethylphosphate at low concentrations of total metabolites. The correlation between the maximum concentrations of total metabolites, measured in urine of poisoned persons on the day of admission to hospital or a day later, and the initial depression of serum cholinesterase (EC 3.1.1.8) and erythrocyte acetylcholinesterase (EC 3.1.1.7) activities was poor (r = 0.6).

A comparative study of trace enrichment of chlorophenols in water by extraction with C6 and C8 alkanes and by C18 reversed-phase adsorption

The efficiency, reproducibility and sensitivity ofn-hexane and iso-octane extraction and of C18 reversed-phase adsorption for accumulation of 4-chloro-, 2,4-dichloro-, 2,4,5- and 2,4,6-trichloro-, 2,3,4,6-tetrachloro- and pentachlorophenol from aqueous solutions were compared. In extraction procedures the acetyl and pentafluorobenzoyl derivatives of chlorophenols were extracted from water. In adsorption procedure chlorophenols adsorbed on a Sep-Pak C18 cartridge were eluted with acetone and after that derivatized analogously.All three procedures were found to be applicable for an efficient trace enrichment of chlorophenols in water, the proper choice being dependent on the required sensitivity of the analysis. Lower detection limits of single compounds at ≈10 ng·1−1 levels were achieved by adsorption procedure owing to the more uniform and for most chlorophenols higher adsorption than extraction recoveries as well as owing to the possibility of treating larger volumes of water samples. The extraction procedure could be successfully applied to the concentrations of chlorophenols in water ≥1μg·1−1.Owing to its higher efficiency and better sensitivity the C18 reversed-phase adsorption procedure was chosen as the more suitable one for the determination of chlorophenol levels in surface, ground and drinking waters. The conversion of chlorophenols accumulated from a water sample parallel to both acetyl and pentafluorobenzoyl derivatives and the analysis of both types of derivatives on two basically different gas Chromatographic columns were recommended for a more reliable identification and quantitation of the compounds analyzed.

Trace enrichment of chlorophenols in human urine by C18 reversed-phase adsorption and by n-hexane extraction

SummaryThe efficiency and sensitivity of C18 reversed-phase adsorption of free chlorophenols and of n-hexane extraction of either free or acetylated chlorophenols from human urine were compared. All procedures were found to be efficient for the trace enrichment of 2,4-dichlorophenol, 2,4,6- and 2,4,5-trichlorophenols, 2,3,4,6- and 2,3,4,5-tetrachlorophenols and pentachlorophenol. The recoveries of chlorophenols from non-hydrolysed and acid hydrolysed urine samples were comparable. By treatment of 1 ml urine sample detection limits of 1–2 ng/ml were achieved, while the treatment of 5 ml samples enhanced the detection sensitivity to less than 1 ng/ml. The n-hexane extraction of acetylated chlorophenols from 1 ml urine samples is the simplest and fastest procedure because the acetylation and extraction of chlorophenols are performed simultaneously in one step. The C18 adsorption seems to be more suitable than n-hexane extraction for accumulation of chlorophenols from a urine volume of 5 ml and higher because the elution is performed always with the same small volume of acetone. Both C18 adsorption and n-hexane extraction procedures were applied for analysis of chlorophenols in general population and in persons with possible occupational exposure to organochlorine compounds.

Occupational Exposure Control by Simultaneous Determination of N-methylcarbamates and Organophosphorus Pesticide Residues in Human Urine

On-column transesterification with methanol was applied for the gas chromatographic determination of N-methylcarbamates extracted from human urine. Transesterification conversion efficiencies of N-methylcarbamates dioxacarb, carbofuran and OMS-22, calculated from the amount of the on-column produced O-methyl-N-methylcarbamate (DMC), were 96, 77 and 76% with detection limits of 8, 10 and 10 ng, respectively. In the investigated concentration range of 0.2-3 micrograms/ml of urine the extraction efficiencies with methylene chloride were independent of the initial concentration of N-methylcarbamate added to urine samples of non-exposed persons. The recoveries and rel. S.D. were 74 +/- 11, 64 +/- 8 and 79 +/- 12% for dioxacarb, carbofuran and OMS-22, respectively. The procedure was applied for the gas chromatographic determination of carbofuran and its metabolites containing the N-methylcarbamic group extracted from urine samples of occupationally exposed persons in a pesticide formulating plant. The level of extracted N-methylcarbamates and the concentration of degradation products of organophosphorus pesticides detected in the urine of the same persons were correlated with the blood and plasma cholinesterase activities. Although the determination of DMC includes only a smaller part of the excreted N-methylcarbamate, a simultaneous determination of both carbamates and organophosphorus residues made it possible to distinguish the cause of depression in cholinesterase activity, indicating early and specifically the exposure to a particular group of agents hazardous to health.

Polychlorinated biphenyls, dibenzo-p-dioxins and dibenzofurans in soil samples from airport areas of Croatia

Levels and patterns of polychlorinated biphenyls (PCBs) were studied in surface soil samples collected in the coastal part of Croatia within and surrounding four different airports and in the vicinity of two partially devastated electrical transformer stations. The compounds accumulated from air-dried soil samples by multiple ultrasonic extraction with an n-hexane : acetone 1 : 1 mixture were analysed by capillary gas chromatography with electron capture and ion-trap detection. PCBs were quantified against a standard Aroclor 1242/Aroclor 1260 mixture and a standard mixture of 17 individual PCB congeners (IUPAC No.: 28, 52, 60, 74, 101, 105, 114, 118, 123, 138, 153, 156, 157, 167, 170, 180, and 189). The mass fractions of total PCBs in 18 soil samples collected within the airport premises ranged from 3 to 41 327 µg/kg dry weight (dw) (median: 533 µg/kg dw), and those in 21 samples collected at a distance ranging from several metres to 5 km away from the airport fence, from <1 to 39 µg/kg dw (median: 5 µg/kg dw). The highest PCB levels were determined in soils along the airport aprons where the aircrafts were serviced and refuelled. The PCB pattern was very similar to technical Aroclor 1260 in all airport soils. The PCB pattern in 22 soils collected in the vicinity of electrical transformer stations was dominated by congeners contained in Aroclor 1242. These soils contained 7 to >400 µg/kg dw of total PCBs. One highly PCB-contaminated airport soil sample was analysed for polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs). With an international toxic equivalent (I-TEQ) of 9.7 ng/kg dw, the airport soil contamination was within values typical for urban and rural areas, and the congener patterns gave no clear indication for PCBs as the only source of PCDDs/PCDFs.

A Test for Monitoring Traces of Cholinesterase Inhibitors in Surface Waters

SummaryThe inhibitory effect on cholinesterase activity is the only common attribute of organophosphorus pesticides and carbamates. Therefore a screening test based on cholinesterase assay is suitable for detection of total pesticides in the pollution control of surface waters. The reaction-rate cholinesterase assay in which acetylthiocholine iodide is used as substrate and 5,5′-dithio-bis (2-nitrobenzoic acid) (Ellmans reagent) as indicator, with spectrophotometric monitoring at 412 nm for 2 min is applied. The detection limits for various pesticides in aqueous solutions have been determined. The results are comparable to those of gas Chromatographic analyses and for carbamates are even better. The sensitivity can be improved by two orders of magnitude by preconcentration on Amberlite XAD-4 column. The collection efficiency of about 80% for all the pesticides tested has been confirmed by gas chromatography. A rapid and simple field test is based on the same assay system. The reaction is stopped by complete inhibition of the enzyme and the colour is compared visually with that of standards prepared by dilution of the initial enzyme solution, and the comparison is facilitated by use of a red filter (λmax 555 nm). A relative standard deviation of 5.5% was obtained for 3 series of sample covering the range 0–100% inhibition, 9 experiments done by 6 persons.ZusammenfassungDer hemmende Effekt gegenüber Cholinesterase ist das einzige gemeinsame Kennzeichen phosphor-organischer Pestizide und Carbamate. Der Nachweis mit Cholinesterase eignet sich daher für den Nachweis von Pestiziden bei der Reinheitskontrolle von Oberflächengewässern. Der Nachweis mit Acetylthiocholinjodid als Substrat und 5,5′-Dithio-bis(2-nitrobenzoe-säure) (Ellmans Reagens) als Indikator durch spektrophotometrische Bestimmung bei 412 nm wurde angewendet. Die Erfassungsgrenzen für verschiedene Pestizide in wäßriger Lösung wurden bestimmt. Die Ergebnisse sind mit denen gaschromatographischer Analysen vergleichbar, für Carbamate sogar besser. Die Empfindlichkeit kann durch Anreicherung mit Amberlit XAD-4 um zwei Größenordnungen verbessert werden. Die Anreicherung um ungefähr 80% wurde gaschromatographisch für alle untersuchten Pestizide bestätigt. Ein schneller und einfacher Feldversuch beruht auf demselben Reaktionsvorgang. Die Reaktion wird durch vollständige Hemmung des Enzyms abgebrochen und die Farbe visuell verglichen mit verdünnten Standardlösungen der ursprünglichen Enzymlösung. Dieser Vergleich wird durch ein Rotfilter (λmax 555 nm) erleichtert. Eine relative Standardabweichung von 5,5% wurde für 3 Probenreihen mit einem Hemmungseffekt von 0–100% erhalten, wobei 6 Personen 9 Versuche durchführten.