Evidence of in vitro metabolic interaction effects of a chlorfenvinphos, ethion and linuron mixture on human hepatic detoxification rates.

General population exposure to pesticides mainly occurs via food and water consumption. However, their risk assessment for regulatory purposes does not currently consider the actual co-exposure to multiple substances. To address this concern, relevant experimental studies are needed to fill the lack of data concerning effects of mixture on human health. For the first time, the present work evaluated on human microsomes and liver cells the combined metabolic effects of, chlorfenvinphos, ethion and linuron, three pesticides usually found in vegetables of the European Union. Concentrations of these substances were measured during combined incubation experiments, thanks to a new analytical methodology previously developed. The collected data allowed for calculation and comparison of the intrinsic hepatic clearance of each pesticide from different combinations. Finally, the results showed clear inhibitory effects, depending on the association of the chemicals at stake. The major metabolic inhibitor observed was chlorfenvinphos. During co-incubation, it was able to decrease the intrinsic clearance of both linuron and ethion. These latter also showed a potential for metabolic inhibition mainly cytochrome P450-mediated in all cases. Here we demonstrated that human detoxification from a pesticide may be severely hampered in case of co-occurrence of other pesticides, as it is the case for drugs interactions, thus increasing the risk of adverse health effects. These results could contribute to improve the current challenging risk assessment of human and animal dietary to environmental chemical mixtures.

Assessment of acetylcholinesterase activity in Clarias gariepinus as a biomarker of organophosphate and carbamate exposure.

The objective of this study was to investigate the response of acetylcholinesterase (AChE) activities in Clarias gariepinus in response to Organophosphates (Ops) and carbamate exposure. The AChE activities were determined in plasma, and eye and brain homogenates of unexposed and exposed fish using Ellman's method and 5,5'-dithiobis-2-nitrobenzoic acid (DTNB) chromophore. The baseline AChE activities in plasma, eyes and brain tissues in unexposed fish were comparable between males and females (P > 0.05). Concentrations of pesticides that inhibited 50% (IC(50)) of AChE activities in brain homogenates following in vitro exposures were 0.003, 0.03, 0.15, 190, 0.2, 0.003 and 0.002 microM for carbaryl, chlorfenvinphos, diazinon, dimethoate, fenitrothion, pirimiphosmethyl and profenofos, respectively. The in vivo dose-effect relationships were assessed using chlorfenvinphos and carbaryl at different concentrations that ranged from 0.0003 to 0.06 microM and 0.0005 to 0.05 microM, respectively. Acetylcholinesterase activities were comparable in plasma, and eye and brain homogenates from control and carbaryl-exposed fish. Following exposure of fish to chlorfenvinphos at concentrations above 0.03 microM, a significant inhibition of AChE activities in plasma (84%) and eye homogenate (50%) was observed. The AChE activities in brain homogenate were comparable between chlorfenvinphos-exposed fish and controls. Because carbaryl cause reversible inhibition of AChE activities was found to be more potent than chlorfenvinphos that cause irreversible inhibition following in vitro exposure. Contrary, carbaryl was less potent than chlorfenvinphos after in vivo exposure possibly due to more rapid biotransformation of carbaryl than chlorfenvinphos. Findings from this study have demonstrated that inhibition of AChE activity in C. gariepinus is a useful biomarker in assessing aquatic environment contaminated by anticholinesterases.

Biosensor-controlled degradation of chlorpyrifos and chlorfenvinfos using a phosphotriesterase-based detoxification column.

This works presents the development of a detoxification system based on bacterial phosphotriesterase (PTE) for the degradation of organophosphate (OP) insecticides in water. PTE was immobilised on an activated agarose gel via covalent coupling. Two different OPs were studied, chlorpyrifos and chlorfenvinfos, due to their importance in the field of water policy. The efficiency of insecticide degradation was controlled using a highly sensitive biosensor allowing the detection of OP concentration as low as 0.004 microgL(-1). Under optimum conditions, it was shown that a column incorporating 500IU of PTE was suitable for the detoxification of solutions containing either isolated pesticides or pesticides mixtures, even at concentrations higher than authorized limits. Finally, the method was shown to be adapted to the decontamination of real samples of pesticides with concentrations up to 20 microgL(-1).

Structure-based rational design of a phosphotriesterase.

In silico substrate docking of both stereoisomers of the pesticide chlorfenvinphos (CVP) in the phosphotriesterase from Agrobacterium radiobacter identified two residues (F131 and W132) that prevent productive substrate binding and cause stereospecificity. A variant (W131H/F132A) was designed that exhibited ca. 480-fold and 8-fold increases in the rate of Z-CVP and E-CVP hydrolysis, respectively, eliminating stereospecificity.

Impact of biotransformation and bioavailability on the toxicity of the insecticides alpha-cypermethrin and chlorfenvinphos in earthworm.

Knowledge about the bioavailability and metabolism of pesticides in soil organisms facilitates interpretation of its toxicity in soil. The present study relates uptake kinetics and metabolism of two insecticides, the pyrethroid alpha-cypermethrin (alpha-CYP) and the organophosphate chlorfenvinphos (CFVP), in the earthworm Eisenia fetida to their lethal and sublethal toxicity. Experiments were conducted in two soils with different organic matter contents to provide media with contrasting sorption capacity for the insecticides. The results showed that organophosphate CFVP was, when taken up by earthworms, rapidly and irreversibly bound to biomolecules and the fraction of extractable parent insecticide and metabolites was low. In contrast, alpha-CYP was rapidly metabolized by earthworms but did not form conjugates. It seems that the phase II metabolism of alpha-CYP is inhibited in earthworms, resulting in an increasing accumulation of its metabolites. Instantaneous binding of non-altered CFVP to the target site presumably resulted in a higher toxicity compared to alpha-CYP and explains the small difference between lethal and reproduction toxicity. For alpha-CYP, however, accumulation of alpha-CYP metabolites in earthworms during chronic exposure may explain the large observed difference between lethal and sublethal toxicity. Bioaccumulation and toxicity of either insecticide decreased with increasing organic matter content in soil, emphasizing the role of compound sorption on bioavailability and toxicity for soil organisms.

Albumin binding as a potential biomarker of exposure to moderately low levels of organophosphorus pesticides.

We have evaluated the potential of plasma albumin to provide a sensitive biomarker of exposure to commonly used organophosphorus pesticides in order to complement the widely used measure of acetylcholinesterase (AChE) inhibition. Rat or human plasma albumin binding by tritiated-diisopropylfluorophosphate ((3)H-DFP) was quantified by retention of albumin on glass microfibre filters. Preincubation with unlabelled pesticide in vitro or dosing of F344 rats with pesticide in vivo resulted in a reduction in subsequent albumin radiolabelling with (3)H-DFP, the decrease in which was used to quantify pesticide binding. At pesticide exposures producing approximately 30% inhibition of AChE, rat plasma albumin binding in vitro by azamethiphos (oxon), chlorfenvinphos (oxon), chlorpyrifos-oxon, diazinon-oxon and malaoxon was reduced from controls by 9+/-1%, 67+/-2%, 56+/-2%, 54+/-2% and 8+/-1%, respectively. After 1 h of incubation with 19 microM (3)H-DFP alone, the level of binding to rat or human plasma albumins reached 0.011 or 0.039 moles of DFP per mole of albumin, respectively. This level of binding could be further increased by raising the concentration of (3)H-DFP, increasing the (3)H-DFP incubation time, or by substitution of commercial albumins for native albumin. Pesticide binding to albumin was presumed covalent since it survived 24 h dialysis. After dosing rats with pirimiphos-methyl (dimethoxy) or chlorfenvinphos (oxon) (diethoxy) pesticides, the resultant albumin binding were still significant 7 days after dosing. As in vitro, dosing of rats with malathion did not result in significant albumin binding in vivo. Our results suggest albumin may be a useful additional biomonitor for moderately low-level exposures to several widely used pesticides, and that this binding differs markedly between pesticides.

Partial degradation of five pesticides and an industrial pollutant by ozonation in a pilot-plant scale reactor.

Aqueous solutions of a mixture of several pesticides (alachlor, atrazine, chlorfenvinphos, diuron and isoproturon), considered PS (priority substances) by the European Commission, and an intermediate product of the pharmaceutical industry (alpha-methylphenylglycine, MPG) chosen as a model industrial pollutant, have been degraded at pilot-plant scale using ozonation. This study is part of a large research project [CADOX Project, A Coupled Advanced Oxidation-Biological Process for Recycling of Industrial Wastewater Containing Persistent Organic Contaminants, Contract No.: EVK1-CT-2002-00122, European Commission, http://www.psa.es/webeng/projects/cadox/index.html] founded by the European Union that inquires into the potential coupling between chemical and biological oxidations for the removal of toxic or non-biodegradable contaminants from water. The evolution of pollutant concentration, TOC mineralization, generation of inorganic species and consumption of O3 have been followed in order to visualize the chemical treatment effectiveness. Although complete mineralization is hard to accomplish, and large amounts of the oxidant are required to lower the organic content of the solutions, the possibility of ozonation cannot be ruled out if partial degradation is the final goal wanted. In this sense, Zahn-Wellens biodegradability tests of the ozonated MPG solutions have been performed, and the possibility of a further coupling with a secondary biological treatment for complete organic removal is envisaged.

[Degradation regulation of fenthion and chlorfenvinfos combined pollutants in red soil].

The degrading regulations of combined pollutants of chlorfenvinfos and fenthion in red soil were studied, in which soil incubation, gas chromatography with nitrogen-phosphorus detection for analysis are utilized. The main conclusions drawn are as follows: under combined pollution condition, the degrading amount of fenthion was significantly higher than that of fenthion alone in soil; under saturated soil humidity, the degrading amount of fenthion was less changed, while that of chlorfenvinfos was increased by 33.3% - 1250%. Soil drought made degradation amount of fenthion decreased a little, while made chlorfenvinfos increased significantly prior to the 21st day after addition of pesticide; nitrogen fertilizer application stimulated both fenthion and chlorfenvinfos degraded; the chemical degrading amount of fenthion in soil with organic matter eliminated was decreased by 22.4% - 30.8%, while that of chlorfenvinfos was increased 42.1% - 2370% at the earlier stage, and was decreased 11% - 17.3% at the later stage. Therefore, there are differences of degrading regulation between single pesticide pollutant and combined pesticide pollutants in soil, and the degradation of organophosphorus pesticides in combined pollutants are influenced with each other.

Influence of cow manure and composts on the effects of chlorfenvinphos on field crops.

Cauliflower crops were grown in several regions and seasons (spring and summer). Five days after planting, the plants were treated against the root fly by pouring onto soil around the plant stem an emulsion of chlorfenvinphos [2-chloro-1-(2,4-dichlorophenyl) ethenyl diethyl phosphate] in water. The fields were divided into plots. Onto each plot, one of the organic fertilizers, city refuse compost, mushroom cultivation compost, or cow manure was applied at the rate of 100 tons/ha, 1 or 3.5 months before the insecticide treatment. There were also control plots which were not treated with any of the organic fertilizers. During the first 50 days crop period which followed the insecticide treatment, the chlorfenvinphos soil concentrations were always greater in the organic fertilizer-treated plots, than in the untreated ones (controls). The intensity of the organic fertilizers effect as to the increase of chlorfenvinphos soil persistence was in the following increasing order: city refuse compost less than cow manure less than mushroom cultivation compost. The organic fertilizer effects were greater when they had been soil-incorporated 3.5 months--instead of 1 month--before the chlorfenvinphos soil treatment. The increase of the insecticide soil concentrations--due to the organic fertilizers treatments--should increase the plant protection efficiency during the period of the first 50 days, during which time the young plants are the most sensitive to insects.(ABSTRACT TRUNCATED AT 250 WORDS)

Metabolic induction of the hepatic cytochrome P450 system by chlorfenvinphos in rats.

Previous studies have shown that a single oral pretreatment of rats with the organophosphorus insecticide 2-chloro-1-(2,4-dichlorophenyl)vinyl diethyl phosphate (chlorfenvinphos, CVP) afforded protection against the toxicity of a subsequent challenge with the same compound within 24 hr. This protection may be due to the reduction in brain cholinesterase inhibition caused by the decrease in plasma CVP concentration. The purpose of this study was to investigate the mechanism of the decrease in plasma CVP concentration in relation to metabolic induction. CVP was preferentially metabolized by a liver microsomal fraction with an NADPH-generating system, compared with serum or kidney subcellular fractions. A single oral 24-hr pretreatment with CVP (15 mg/kg) increased the oral LD50 of its next dosage to threefold. The same treatment also increased CVP metabolism (to 178%), cytochrome P450 content (to 130%), cytochrome P450 reductase activity (to 130%), cytochrome b5 content (to 121%), and cytochrome P450-linked activities such as aminopyrine demethylase (to 140%) and aniline hydroxylase (to 127%) in the hepatic microsomal fraction. A single oral 24-hr pretreatment of phenobarbital (50 mg/kg), which is known as an inducer of cytochrome P450, increased the oral LD50 of CVP and all the related metabolic parameters listed above in an order of magnitude similar to that of CVP, although the increments induced by the phenobarbital treatment were greater than those induced by the CVP treatment. These results indicate that the increase in hepatic CVP metabolism may be due to the induction of the hepatic cytochrome P450 system caused by the single oral short-term treatment with CVP. This induction may be one of the reasons for the decrease in plasma CVP concentration which may be responsible for the reduction in toxicity of its next dosage.

Detoxification of the organophosphorus insecticide chlorfenvinphos by rat, rabbit and human liver enzymes.

A good inverse correlation between the acute oral toxicity of chlorfenvinphos and its rate of oxidative detoxification in the liver exists for rats, mice, rabbits and dogs. Measurements of the rates of oxidative metabolism (O-de-ethylation) by in vitro liver preparations from rat, rabbit and human have been compared. When the results are expressed in terms of cytochrome P450, as opposed to microsomal protein, detoxification by the human liver enzyme(s) is almost as effective as that by rabbit enzyme(s). The rabbit is relatively resistant to the acute toxic action of the insecticide.

Sites of methylation of DNA bases by the action of organophosphorus insecticides in vitro.

Methylation in vitro of DNA by three methyl-14C-labelled organophosphorus insecticides has been studied. The ability of methylbromphenvinphos, methylparathion and malathion to methylate N-7 of guanine in DNA can be expressed as 100:40:15. Among the methylation products, no O6-methylguanine, a known mutagen, was found. Both in the reaction with dsDNA and with ssDNA 7-methyl-guanine was the main methylation product. However, all methyl derivatives of adenine (3-methyladenine, 1-methyladenine and 7-methyladenine) constituted about 40% and 50% of all methylation products in the case of dsDNA and ssDNA, respectively. The only methyl derivative of pyrimidine we have identified was 3-methylcytosine. In the case of dsDNA 3-methylcytosine appeared in small amounts but in the alkylated ssDNA 3-methylcytosine C constituted about 20% of all alkylation products.

Theoretical aspects of enzyme induction and inhibition leading to the reversal of resistance to biocides.

The well-known phenomena of enzyme induction and inhibition have been applied in the enunciation of two mechanisms which could be used in the reversal of resistance which organisms develop towards biocides (drugs and pesticides) in many cases. For those biocides active per se which are metabolized by inducible enzymes to non-toxic metabolites, resistant organisms would be those possessing high levels of drug-metabolizing enzymes (Mechanism 1). For those biocides inactive per se but requiring metabolic activation for activity, resistant organisms would be those possessing low levels of drug metabolizing enzymes (Mechanism 2). In mechanism 1, the addition of enzyme inhibitors to the biocide would be effective in reversing resistance. In mechanism 2 the addition of an enzyme inducer to the biocide would increase the susceptibility of the resistant organisms. An ectoparasite insecticide 2-chloro-1-(2,4 dichlorophenyl) vinyl diethylphosphate (chlorfenvinphos or supona) is used as an example for mechanism 1. The malarial drugs primaquine and chloroquine are used as examples of mechanism 2.

The effect of hepatic microsomal monooxygenase induction on the metabolism and toxicity of the organophosphorus insecticide chlorfenvinphos.

The induction of rat liver microsomal monooxygenase by pretreatment of rats with dieldrin affords a 10-fold protection against the acute toxic effects of the organophosphorus insecticide, chlorfenvinphos. Metabolism studies were carried out to confirm that the protection was due to an enhanced rate of detoxification (via oxidative deethylation). At low doses of chlorfenvinphos (2.5 mg . kg-1), dieldrin pretreatment caused minimal changes in the metabolic profiles. However, at a higher dose (13.2 mg . kg-1), giving clinical signs of intoxication in the control animals, the dieldrin pretreated rats produced 5 times more deethylchlorofenvinphos than did the control animals. The results support the conclusion that the effect of enzyme induction on the metabolism of substrates of that enzyme are dose-dependent. Alterations in metabolism, therefore, are not an automatic consequence of enzyme induction.