Rapid screening method, including automated colorimetry, for low residue levels of linuron and-or chlorpropham in vegetables.
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The gas chromatographic response of four perfluoro derivatives, of four agricultural chemical [diethylstilbestrol] (DES) clopidol, linuron and carbofuran] was examined. The derivatives varied in fluorine content from 3 to 30 atoms per molecule. The sensitivities of the derivatives were found to be ca. 10-100 times greater by electron-capture detection than by electrolytic conductivity detection (halogen mode). The sensitivity also was found to increase with increasing fluorine content for all derivatives by electrolytic conductivity, whereas by electron capture, DES and clopidol exhibited similar responses with either the penta-, hepta-, or pentadeca-fluoro derivatives. The sensitivity of linuron and carbofuran derivatives by electron capture varied with increasing fluorine content. For detection by electron capture, the hepta-fluorobutyryl derivatives were preferred for DES and clopidol, and either the hepta-fluorobutyryl or the pentadecafluorooctanoyl derivatives for linuron and carbofuran. For detection by electrolytic conductivity, the pentadecafluorooctanoyl derivatives were superior for all four compounds.
The phenylurea herbicide linuron is hydrolyzed by Bacillus sphaericus ATCC 12123 quantitatively forming 3,4-dichloroaniline, CO2, and N,O-dimethylhydroxylamine. The inducible enzyme responsible for this hydrolysis was purified to homogeneity as judged by polyacrylamide gel electrophoresis. Its molecular weight was 75 000 +/- 10%. Studies on its substrate specificity showed that either whole cells as the linuron-induced enzyme hydrolyze a large number of herbicidal and fungicidal acylanilides, the methoxysubstituted phenylureas and the phenylcarbamate propham at the carbonyl-aniline bond. This would classify the enzyme as an aryl acylamidase (E.C. 3.5.1). Hydrolysis of phenylamides by whole cells and by the enzyme is inhibited by different methylcarbamate and organophosphorus insecticides. Inhibition of hydrolysis of linuron by the aryl acylamidase by methylcarbamates is a competitive one.
A comparison of gas chromatography with electron-capture or electrolytic-conductivity (nitrogen mode) detection, and high-pressure liquid chromatography (HPLC) with UV-absorption detection (254 nm) was carried out for the analysis of several herbicides in foods. Linuron, propanil, terbacil, benzoylprop-ethyl, and the fungicide DCNA in samples of cabbage, corn, potato, and wheat spiked at 2 and 0.2 ppm were examined. The pesticides were extracted with acetone, partitioned into petroleum ether-methylene chloride, and cleaned up on a 2% deactivated Florisil column before direct chromatographic analysis. Electron-capture gas-liquid chromatography (GLC) was most suitable for DCNA and benzoylprop-ethyl while UV-absorption HPLC was best for terbacil analysis. Linuron and propanil gave similar results for both electron-capture GLC and HPLC. Electrolytic-conductivity GLC could detect all pesticides at the 0.2 ppm level and exhibited the least number of extraneous peaks in the chromatograms.
The degradation of the phenylamide herbicides monolinuron, linuron, and solan by cultures of Bacillus sphaericus ATCC 12123 was inhibited by the methylcarbamate insecticides metmercapturon, aldicarb, propoxur, and carbaryl and by the organophosphorus insecticides fenthion and parathion. The extent of inhibition was largest with metmercapturon and smallest with parathion inhibition of hydrolysis of the two phenylurea herbicides was greater than of the acylanilide compound. Tests with crude enzyme preparations of aryl acylamidase derived from B. sphaericus showed that the inhibition of the hydrolysis of linuron with methylcarbamates is a competitive one. The insecticides tested did induce the enzyme, nor could they serve as its substrate.
Recommended concentrations of paraquat alone and its combination with each of linuron, diuron, atrazine, simazine, and simazine plus diuron exerted little effect on total populations of bacteria, actinomycetes, and fungi in Fox sandy loam under laboratory and simulated field conditions in 66 and 77 days, respectively. Respiration of the total microbiota in soil suspension was afeected by the combinations as well as individual herbicides in various concentrations. Yet, the inhibition of the O2 uptake by any of these herbicides, including some extreme concentrations, was not permanent, indicating adaptation, or suppression of specific organisms. Only linuron in concentrations up to 20 microng/ml stimulated respiration of the soil.
A fluorescence-staining technique using the magnesium salt of 8-anilino-1-naphthalene sulfonic acid is described and used to follow the changes in the distribution patterns of microorganisms in soils. A statistical procedure was used to determine the occurrence of significant differences in clumping of bacteria (i.e., production of colonies) in different regions of artificial soil-aggregate systems treated with nutrient solutions and also with a herbicide, Linuron. The response of soil microorganisms to glucose amendment was most marked in the aerobic, outer zone of aggregates. Linuron inhibited colony formation in aggregates treated with the herbicide. The method allows continued observations to be made on the same soil sample at intervals during incubation and os can be used to determine growth rates, inhibitory effects of chemicals, distribution patterns in soils, effects of added nutrients, and other effects where growth in situ is important.
A Gram- negative rod-shaped bacterium 28/1 isolated by enrichment cultures is able to hydrolyze the amide bond of some phenylurea herbicides and acid anilide herbicides by an inducible amidase. 7.5% of 0.3 mumol.ml-1 linuron (3-(3,4-dichlorophenyl)-1-methoxy-1-methylurea) are hydrolyzed after 16 hours. 1,1-Dimethylphenylureas are not degraded. Acid anilides are hydrolyzed at a higher rate, 80% of 0.5 mumol.ml-1 N-(4-chlorophenyl)-propionamide and N-(4-nitrophenyl)-propionamide are transformed after 6 hours. The 1-methoxy-1-methyl phenylureas are effective inducers. Linuron-induced cells have a specific activity of 3-4 nmol per mg dry weight per min on the substrate N-(3,4-dichlorophenyl)-propionamide (Propanil). The rate of hydrolysis is influenced by substituents of the aniline ring and by the structure of the side chain of the acid anilides.
High-flow pneumatically assisted electrospray (ESP) was applied to the characterization of triazine (atrazine, simazine, ametryne, cyanazine, deethylatrazine and deisopropylatrazine), phenylurea (chlortoluron++, isoproturon, diuron, linuron and diflubenzuron) and other priority herbicides (alachlor, metolachlor). In LC-ESP-MS the [M+Na]+ ion was used as the base peak in most cases, with the exception of chlorotriazines, which showed [M+H]+ as the base peak. When LC-TSP-MS was used, [M+H]+ was the base peak for many of the pesticides, with the exception of linuron and diflubenzuron, which showed [M+NH4]+ as the base peak. The ESP results were compared with those obtained with thermospray (TSP). LC-TSP-MS offered greater sensitivity for triazines than phenylurea herbicides, whereas the use of LC-ESP-MS offered an enhancement in sensitivity for phenylurea herbicides. As regards the fragmentation obtained using both techniques, ESP offered a considerable amount of structural information for the different chlorotriazines studied when the extraction voltage was increased from 20 to 40 V. Liquid-liquid extraction with dichloromethane was used for the trace enrichment of the different herbicides in estaurine water samples from the Elorn river (France). The presence of the different triazine metabolites, atrazine, simazine, metolachlor, isoproturon and diuron was confirmed by both LC-MS techniques.
Glutathione (GSH) plays a central role in the chemical detoxication. Xenobiotics which induce GSH depletion, either via GSH conjugation or via oxidation of GSH to glutathione disulfide (GSSG), alter the mechanism of natural cellular defence against toxicants. The aim of this study was to evaluate the ability of seven widely used pesticides (Alachlor, Atrazine, Benomyl, Captan, Linuron, Methyl Parathion and Propanil) and/or of their metabolites to deplete GSH in rat liver fractions. In our experimental conditions, Atrazine, Linuron and Propanil failed to interact with rat liver GSH. Conversely, Alachlor, Benomyl and Methyl Parthion were able to deplete GSH in rat liver, probably by forming GSH conjugates. The fungicide Captan rapidly reduced the rat liver concentration of GSH by converting it to the oxidized form GSSG. But a longer incubation of Captan with rat hepatic enzymes produced the formation of metabolites which depleted GSH via conjugation. Our results suggest that exposure to the pesticides Alachlor, Benomyl, Captan and Methyl Parathion may induce an alteration of natural mechanisms of defence against toxicants in mammals, including humans.
Cytopathological alterations in proximal (PS I, PS II) and distal segments (DS) of rainbow trout (Oncorhynchus mykiss) renal tubules following exposure to 0, 10, 20, 40, 80, and 160 micrograms/liter atrazine for 4 weeks were investigated by means of electron microscopy. Cellular responses were clearly dose-dependent with a gradual increase in variability and intensity of effects. Ultrastructural modifications in PS I and II were observed from 10 micrograms/liter atrazine, in DS from 20 micrograms/liter. In PS I, major changes included proliferation of smooth endoplasmic reticulum, atypical mitochondria and lysosomes, as well as gradual alterations of the apical plasmalemma. Typical changes in PS II cells were a proliferation of peroxisomes and ring- and cup-shaped mitochondria, as well as alterations in the basal labyrinth; DS cells were characterized by a proliferation of atypical mitochondria with longitudinally oriented cristae, disorganization of Golgi fields and vacuolization of the cell base. Results document that different segments of the renal tubule in rainbow trout react not only with different levels of sensitivity to atrazine exposure, but also in a segment-specific way. Moreover, comparison of effects induced by atrazine with those resulting from chronic exposure to the herbicide linuron revealed a distinct substance specificity in the reaction of different tubular segments.
A quality assurance program was developed for two grantee laboratories studying the herbicides atrazine and linuron in Chesapeake Bay water. Proposed methodologies were evaluated by performance and system audits. The objectives of the quality assurance program and the results of the audit program are discussed.
From Bacillus sphaericus ATCC 12123 an aryl acylamidase (EC 3.5.1.13) was purified to homogeneity by ion exchange chromatography, gel filtration, and polyacrylamide gel electrophoresis. The enzyme is inducible by various phenylamides of the acylanilide, phenylcarbamate, and methoxysubstituted phenylurea type. It has a molecular weight of 75,000. Enzyme activity was inhibited by sulfhydryl reagents, several metal ions, and 3,4-dichloroaniline (a product of linuron degradation). A requirement for divalent metal ions in enzyme activity could not be demonstrated. In the presence of 6 M urea an irreversible inactivation of the enzyme occurred. The hydrolysis of L-alanine-4-nitroanilide was competitively inhibited by puromycin.