The effect of two bromfenvinphos impurities: BDCEE and ß-ketophosphonate on oxidative stress induction, acetylcholinesterase activity, and viability of human red blood cells.

Numerous research works have shown that synthesis of pesticides leads to the formation of impurities that may substantially enhance pesticide toxicity. In this study, the effect of manufacturing impurities of pesticide bromfenvinphos (BFVF) such as 1-bromo-2-(2,4-dichlorophenyl)-2-ethoxy ethene (BDCEE) and diethyl [2-(2,4-dichlorophenyl)-2-oxo-ethyl] phosphonate (ß-ketophosphonate) on human erythrocytes, being significantly exposed to xenobiotics has been studied. The cells were treated with the compounds studied in the concentrations ranging from 0.1 µM to 250 µM for 4 h. In order to assess the effect of BDCEE and ß-ketophosphonate on red blood cells hemolytic changes, changes in cell size (FSC parameter) and oxidation of hemoglobin were studied. Moreover, alterations in reactive oxygen species (ROS) formation, reduced glutathione (GSH) level and acetylcholinesterase (AChE) activity were determined. BDCEE induced an increase in ROS level and caused strong oxidation of hemoglobin as well as a slight change in erythrocytes size and hemolysis, while it did not change GSH level and AChE activity. ß-ketophosphonate has not been shown to affect most parameters studied, but it strongly reduced AChE activity. Because changes in the parameters examined were noted at low concentrations of BFVF impurities (5-250 µM), those substances should not negatively affect on red blood cells of humans environmentally exposed to this pesticide.

A 10 year survey of acaricide residues in beeswax analysed in Italy.

BACKGROUND: The aim of this work was to provide an overview of the prevalence and level of acaricides in beeswax used in Italy in the past 10 years by analysing 1319 beeswax samples processed by the certified laboratory of the Italian Bee Research Institute. RESULTS: The proportion of samples positive to at least one active ingredient decreased between 2005 and 2009 (from 69 to 32%) and then increased again between 2009 and 2014 (from 32 to 91%). This trend is in agreement with reports from beekeepers that the use of synthetic acaricides decreased in the second half of the past decade and increased after the beginning of the colony losses phenomenon. The active ingredient with the greatest overall proportion of positive samples was coumaphos (49%), followed by fluvalinate (38%) and chlorphenvinphos (25%). The indicator for amitraz, 2,4-dimethylphenylformamide (DMPF), was detected in a very small proportion of samples (6%), while residues of cymiazole were never found. CONCLUSIONS: In more than half of the analysed samples, residues of at least one active ingredient were detected. The mean levels of residues of all the considered active ingredients in the positive samples may represent a source of accumulation in beeswax and pose risks to honey bee health. © 2015 Society of Chemical Industry.

Oxidative stress in human erythrocytes treated with bromfenvinphos and its impurities.

Bromfenvinphos (BFVF) is an organophosphorus (OP) pesticide which was widely used in agriculture and veterinary practice. During synthesis of this insecticide five main impurities are formed: dihydro-bromfenvinphos, dibromo-bromfenvinphos, 2,4-dichlorophenacyl bromide, 2,4-dichlorophenacylidene bromide and 2,4-dichlorophenacylidyne bromide, which can be present in technical grade bromfenvinphos in amounts from 0.1 to 4%. The aim of this study was to examine the influence of bromfenvinphos and its manufacturing impurities on parameters of oxidative stress, the activity of antioxidative enzymes and the level of reduced glutathione. Human erythrocytes were incubated with bromfenvinphos and its impurities in the concentrations range from 0.5 to 500 µM for 1 h. This study indicated that 2,4-dichlorophenacyl derivatives more strongly oxidized analyzed parameters in human erythrocytes than bromfenvinphos. Investigated compounds caused an increase in lipid peroxidation and oxidation of fluorescent probe DCFH2 - the strongest pro-oxidative changes were provoked by 2,4-dichlorophenacyl bromide. None of the compounds studied in the concentrations from 0.5 to 500 µM changed the activity of SOD and only 2,4-dichlorophenacyl decreased activity of CAT. The level of GSH was only altered by 2,4-dichlorophenacyl derivatives. It was observed that increasing number of bromine atoms in the side chain of those derivatives was associated with decreased GSH level.

Removal of priority pollutants from water by means of dielectric barrier discharge atmospheric plasma.

Two different nonthermal plasma reactors at atmospheric pressure were assessed for the removal of organic micropollutants (atrazine, chlorfenvinfos, 2,4-dibromophenol, and lindane) from aqueous solutions (1-5 mg L(-1)) at laboratory scale. Both devices were dielectric barrier discharge (DBD) reactors; one was a conventional batch reactor (R1) and the other a coaxial thin-falling-water-film reactor (R2). A first-order degradation kinetics was proposed for both experiments. The kinetic constants (k) were slightly faster in R1 (0.534 min(-1) for atrazine; 0.567 min(-1) for chlorfenvinfos; 0.802 min(-1) for 2,4-dibromophenol; 0.389 min(-1) for lindane) than in R2 (0.104 min(-1) for atrazine; 0.523 min(-1) for chlorfenvinfos; 0.273 min(-1) for 2,4-dibromophenol; 0.294 min(-1) for lindane). However, energy efficiencies were about one order of magnitude higher in R2 (89 mg kW(-1) h(-1) for atrazine; 447 mg kW(-1) h(-1) for c hlorfenvinfos; 47 mg kW(-1) h(-1) for 2,4-dibromophenol; 50 mg kW(-1) h(-1) for lindane) than in R1. Degradation by -products of all four compounds were identified in R1. As expected, when the plasma treatment (R1) was applied to industrial wastewater spiked with atrazine or lindane, micropollutant removal was also achieved, although at a lower rate than with aqueous solutions (k = 0.117 min(-1) for atrazine; k = 0.061 min(-1) for lindane).

The effect of bromfenvinphos, its impurities and chlorfenvinphos on acetylcholinesterase activity.

The aim of this work was to examine the effect of two organophosphorous compounds i.e. bromfenvinphos (BFVF) and chlorfenvinphos (CFVF) possessing acaricidal and insecticidal properties, on the activity of human erythrocytes acetylcholinesterase (AChE, EC 3.1.1.7). Moreover, the effect of five bromfenvinphos production impurities on AChE activity was studied. The erythrocytes were incubated with the compounds studied in the concentrations range from 0.05 to 250 µM for 1h. The organophosphorous compounds studied in low concentrations increased Km value but they did not change Vmax value (competitive inhibition). Higher concentrations of the compounds studied decreased Vmax value and increased Km value, what revealed a mixed type of AChE inhibition by these xenobiotics. Basic significance in AChE activity inhibition has the type of halogen in vinyl group. Chlorfenvinphos (insecticide) exhibited stronger enzyme inhibition than bromfenvinphos. CFVF and dibromo-bromfenvinphos possessed the lowest Ki and Ki' values among all the compounds studied. The presence of Cl atom (chlorfenvinphos) instead of Br atom (bromfenvinphos) considerably increases antiesterase activity of the individual compound. Three impurities like 2,4-dichlorophenacyl bromide, 2,4-dichlorophenacylidene bromide and 2,4-dichlorophenacylidyne bromide did not induce any statistically changes in AChE activity. Two impurities of bromfenvinphos such as: dihydro-bromfenvinphos and dibromo-bromfenvinphos revealed significant effect on the AChE activity, which may be connected with the presence a phosphate group in these substances. It was proven that an increase in antiesterase activitiy of the compounds studied corresponded with the increase in the number of Br atoms at carbon of their vinyl group: dibromo-bromfenvinphos>bromfenvinphos>dihydro-bromfenvinphos.

Development and validation of a rapid and wide-scope qualitative screening method for detection and identification of organic pollutants in natural water and wastewater by gas chromatography time-of-flight mass spectrometry.

In this work, a multiclass screening method for organic contaminants in natural and wastewater has been developed and validated for qualitative purposes, i.e. to ensure the reliable and sensitive identification of compounds detected in samples at a certain level of concentration. The screening is based on the use of GC-TOF MS, and the sample procedure involves solid phase extraction with C(18) cartridges. Around 150 organic contaminants from different chemical families were investigated, including PAHs, octyl/nonyl phenols, PCBs, PBDEs and a notable number of pesticides, such as insecticides (organochlorines, organophosphorus, carbamates and pyrethroids), herbicides (triazines and chloroacetanilides), fungicides and several relevant metabolites. Surface water, ground water and effluent wastewater were spiked with all target analytes at three concentration levels (0.02, 0.1 and 1 µg/L). Influent wastewater and raw leachate from a municipal solid waste treatment plant were spiked at two levels (0.1 and 1 µg/L). Up to five m/z ions were evaluated for every compound. The identification criterion was the presence of, at least, two m/z ions at the expected retention time, measured at their accurate mass, and the accomplishment of the Q/q(i) intensity ratio within specified tolerances. The vast majority of compounds investigated were correctly identified in the samples spiked at 1 µg/L. When analyte concentration was lowered down to 0.1 µg/L the identification was more problematic, especially in complex-matrix samples like influent wastewater. On the contrary, many contaminants could be properly identified at the lowest level 0.02 µg/L in cleaner matrices. The procedure was applied to the screening of water samples of different origin and matrix composition and allowed the detection of several target contaminants. A highly reliable identification could be carried out thanks to the sensitive full-spectrum acquisition at accurate mass, the high selectivity reached with the use of narrow-mass window extracted ion chromatograms, the low mass errors observed in the positive detections and the Q/q ratio accomplishment.

The effect of bromfenvinphos and its impurities on human erythrocyte.

Bromfenvinphos - (E,Z)-O,O-diethyl-O-[1-(2,4-dichlorophenyl)-2-bromovinyl] phosphate (BFVF) is the insecticide elaborated in Poland, which has been used against Varroa destructor causing honey bees disease called as varroosis. The substances that are formed as a result of bromfenvinphos synthesis are dihydro-bromfenvinphos (O,O-diethyl O-[1-(2,4-dichlorophenyl)vinyl] phosphate); dibromo-bromfenvinphos (O,O-diethyl O-[1-(2,4-dichlorophenyl)-2,2-dibromovinyl] phosphate); 2,4-dichlorophenacyl bromide; 2,4-dichlorophenacylidene bromide and 2,4-dichlorophenacylidyne bromide. In this work, we evaluated the effect of these compounds on hemolysis and hemoglobin oxidation (met-Hb formation) in human erythrocytes. Moreover, the changes in the size (FSC-A) and the shape (SSC-A) of red blood cells were assessed using flow cytometry and phase contrast microscopy. It was proven that bromfenvinphos at concentrations ranging from 0.5 to 250 µM during 1h incubation did not change the parameters examined in human erythrocytes. Similarly, most of bromfenvinphos impurities did not increase hemolysis and methemoglobin level nor changed the size and shape of the erythrocytes. The exception was dibromo-bromfenvinphos, which changed the FSC-A and SSC-A parameters, as well as 2,4-dichlorophenacyl bromide which induced hemolysis, increased the level of met-Hb and changed erythrocytes morphology.

Photo-Fenton decomposition of chlorfenvinphos: determination of reaction pathway.

The purpose of this work was to determine the degradation products and pathway of chlorfenvinphos (CFVP) in water treated by photo-Fenton driven by solar irradiation, as well as to develop an analytical procedure for the degradation experiments. Degradation products and pathway were determined in a laboratory experimental setup. Routine water sample analysis was done by standard laboratory wet chemistry procedures and the use of laboratory equipment such as HPLC-UV and ionic chromatography (IC). Solid-phase extraction (SPE) was used to extract analytes from an aqueous matrix, and GC-MS was used to identify intermediate degradation products. The use of an HPLC-TOF-MS provided more results on degradation products and more insight was gained into how degradation takes place. In all experiments, strong mineralisation and degradation of CFVP was observed. CFVP and its degradation products, like 2,4-dichlorophenol, 2,4-dichlorobenzoic acid and triethylphosphate were decomposed into organic substances like acetate, formate, maleate, and inorganic ions like chloride and phosphate, within the detection limits (12.5 microg/L for CFVP in the GC-MS and 40 microg/L in HPLC-UV) of the equipment used. In fact, Cl(-) emerges in nearly stoichiometric concentrations and PO(4)(3)(-) is precipitated as FePO(4). The remarkably complete absence of chlorinated aliphatic substances and chlorinated acids leads to the conclusion that chlorine is removed very quickly, and that residual DOC does not correspond to any chlorinated compound.

Nonexhaustive beta-cyclodextrin extraction as a chemical tool to estimate bioavailability of hydrophobic pesticides for earthworms.

Chemical methods to assess bioavailability in soil and sediment often use synthetic polymers that mimic uptake of organic compounds in organisms or microbial degradation. In this paper we have assessed a biomimetic extraction method using hydroxyl-beta-cyclodextrin (HP-beta-CD) to estimate uptake of the two insecticides alpha-cypermethrin (alpha-CYP) and chlorfenvinphos (CFVP) in the earthworm Eisenia fetida. Additionally, a novel approach was developed to estimate the efficiency of biomimetic extractions. The study revealed that HP-beta-CD is a suitable surrogate for estimating the bioaccessibility of hydrophobic chemicals in soil. If one uses a 3.5 times higher amount of HP-beta-CD than soil, effective and reproducible extractions can be achieved within 48 h. Atthese conditions, inclusion of dissolved chemicals by HP-beta-CD mimics uptake of a given compound into earthworms and takes into account sorption-related aspects that control biological uptake. The data indicate that, with increasing hydrophobicity, the affinity of organic chemicals to HP-beta-CD does not increase to the same degree as to soil organic matter. Therefore, a high surplus of HP-beta-CD is necessaryto provide a sufficient extraction capacity in biomimetic extractions.

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.

Oxidation of chlorfenvinphos in ultrapure and natural waters by ozonation and photochemical processes.

The chemical oxidation of the organophosphorus insecticide chlorfenvinphos, a priority pollutant in aquatic environments, has been conducted in ultrapure water, by means of single degradation agents (ozone and UV radiation), and by the Advanced Oxidation Processes constituted by combinations of these oxidants (O(3)/H(2)O(2) and UV/H(2)O(2)). The influence of the operating variables was discussed, and the degradation rates were evaluated by determining the rate constants for the reactions with ozone (k(O)(3)=3.7+/-0.2 L mol(-1)s(-1)) and OH radicals (k(OH)=(3.2+/-0.2)x10(9) L mol(-1)s(-1)), as well as the quantum yield for the photodegradation (around 0.1 mol E(-1), depending on the pH). Additionally, the ozonation of chlorfenvinphos in a natural water system (a surface water from a reservoir) was studied. The influence of the operating conditions on the insecticide removal efficiency was established, and the R(ct) parameter was evaluated. A kinetic model was proposed for the prediction of the elimination rate of chlorfenvinphos in the ozonation process and the results obtained reveal a good agreement between experimental results and predicted values.

Chlorination of organophosphorus pesticides in natural waters.

Unknown second-order rate constants for the reactions of three organophosphorus pesticides (chlorpyrifos, chlorfenvinfos and diazinon) with chlorine were determined in the present study, and the influence of pH and temperature was established. It was found that an increase in the pH provides a negative effect on the pesticides degradation rates. Apparent second-order rate constants at 20 degrees C and pH 7 were determined to be 110.9, 0.004 and 191.6 M(-1) s(-1) for chlorpyrifos, chlorfenvinfos and diazinon, respectively. A higher reactivity of chlorine with the phosphorothioate group (chlorpyrifos and diazinon) than with the phosphate moiety (chlorfenvinfos) could explain these results. Intrinsic rate constant for the elementary reactions of chlorine species with chlorpyrifos and diazinon were also calculated, leading to the conclusion that the reaction between hypochlorous acid and the pesticide is predominant at neutral pH. The elimination of these pesticides in surface waters was also investigated. A chlorine dose of 2.5 mg L(-1) was enough to oxidize chlorpyrifos and diazinon almost completely, with a formation of trihalomethanes below the EU standard for drinking water. However, the removal of chlorfenvinfos was not appreciable. Therefore, chlorination is a feasible option for the removal of organophosphorus pesticides with phosphorothioate group during oxidation and disinfection processes, but not for the elimination of pesticides with phosphate moiety.

Enhancing biodegradability of priority substances (pesticides) by solar photo-Fenton.

In this paper, we present the photo-Fenton treatment in a solar pilot-plant scale of several EU priority hazardous substances (Alachlor, Atrazine, Chlorfenvinphos, Diuron and Isoproturon) dissolved in water. The results have been evaluated not only from the point of view of contaminant disappearance and mineralisation, but also of toxicity reduction and enhancement of biodegradability. Degradation was monitored by total organic carbon, pesticide concentration by HPLC-UV, inorganics released by ion chromatography, and biodegradability by the Zahn-Wellens (Z-W) test. The total volume of the solar photoreactor, composed of compound parabolic collectors with a total area of 4.16m2, was between 70 and 82 L. The treatment was shown to be effective, mineralising all of the pesticides tested, both alone and in mixtures. In order to find out the conditions for biocompatibility using the photo-Fenton reaction as a pre-treatment step, wastewater inoculated with unacclimated municipal sludge containing pesticides after certain degradation time was evaluated by the Z-W test. Biodegradability was enhanced (70% considered biodegradable) by the photo-Fenton treatment after 12-25min. It may be concluded that the photo-Fenton treatment consistently enhances biodegradability of wastewater containing pesticides.