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At least 433 records · Page 24Linked to original sources

Mutagenic activity of the Ganges water with special reference to the pesticide pollution in the river between Kachla to Kannauj (U.P.), India.

Water samples from Ganga river were collected from 3 different locations viz. Kachla, Fatehgarh and Kannauj (U.P.). High performance liquid chromatography analysis of samples by liquid-liquid extraction procedure showed the presence of some pesticides like DDT, alpha-BHC, aldrin, dieldrin etc. DDT, alpha-BHC, DDD, aldrin and dieldrin were present at concentration ranges of 3.33-5.33 ppb, 1.73-3.01 ppb, 0.88-2.41 ppb, 1.17-2.81 ppb and 0.49-4.11 ppb, respectively. The organophosphorus pesticides like dimethoate and methyl parathion were also detected at the concentration levels of 0.41-0.56 ppb and 0.16-0.50 ppb, respectively. The organic substances in the test samples were extracted by XAD-resin and liquid-liquid extraction procedures, and the extracts were assayed for mutagenic potential by the Ames Salmonella/microsome test. The test samples exhibited a remarkable degree of mutagenicity with TA98, TA100 and TA97a strains with the probable role of contaminating pesticides in the river water.

Base Composition↗

The effects of 2,4-D herbicide and organophosphorus insecticides on growth, photosynthesis, and chlorophyll a synthesis of Chlamydomonas reinhardtii (mt +).

The effects of the herbicide (2,4-D) and six organophosphorus insecticides (Diazinon, Dimethoate, Fenitrothion, Malathion, Phenthoate and Quinalphos) on growth, photosynthesis and chlorophyll a synthesis of the fresh water green alga Chlamydomonas reinhardtii (mt +) were studied. At low concentrations (1 and 5 ppm), the herbicide and all six orgnophosphorus insecticides stimulated photosynthesis of the alga. The stimulating effects on algal growth and chlorophyll a synthesis were only observed in the presence of low concentration (1 ppm) of 2,4-D and Fenitrothion, Growth, photosynthesis and chlorophyll a synthesis of the alga were inhibited in the presence of high concentrations (10, 20 and 40 ppm) of the herbicide and all the six organophosphorus insecticides. Results also indicated that the toxicities of these organophosphorus insecticides on the tested alga were dependent on their chemical structures.

Journal Article↗

Cytogenetic effects induced by organophosphorus pesticides in mouse spermatocytes.

Male mice (Q strain) received a single i.p. injection of 14 organophosphorus compounds, including 11 insecticides, administered on separate occasions. After a recovery period of 10 to 15 days, the cytogenic effects were analyzed in primary spermatocytes at diakinesis-metaphase I corresponding to the treatment of A4-B type spermatogonia. At the highest tolerated dose, trimethylphosphate (1000 mg/kg), triethylphosphate (300 mg/kg), dichlorvos (10 mg/kg), methylparathion (10 mg/kg), ethylparathion (10 mg/kg), ethylparaoxon (0.3 mg/kg), fenitrothion (1000 mg/kg), methylbromophos (1000 mg/kg), ethylbromophos (1000 mg/kg), dimethoate (10 mg/kg), malathion (300 mg/kg), methylazinphos (1 mg/kg), ethylazinphos (1 mg/kg) and trichlorfon (100 mg/kg) did not produce chromosome damage.

Animals↗

Effect of carbon disulfide on the anticholinesterase action of several organophosphorus insecticides in mice.

Effect of carbon disulfide (CS2) on toxic action of 11 organophosphorus (OP) insecticides were examined by determining the plasma cholinesterase activity in mice. CS2 pretreatment potentiated the anticholinesterase action of parathion and EPN, but suppressed that of dimethoate and diazinon. CS2 had no significant effect or a slightly suppressive effect on the other compounds. Some of these effects were contrasted with the reported alteration of the toxicity following phenobarbital pretreatment. CS2 administration suppressed both detoxification and activation of parathion and EPN by liver microsomes in vitro, as measured by p-nitrophenol production and cholinesterase inhibition, respectively. Causal relationship between the in vitro and in vivo observations, however, remains to be clarified.

Animals↗

Cell proliferation as a determining factor for the carcinogenicity of chemicals: studies with mutagenic carcinogens and mutagenic noncarcinogens.

Recent work in our laboratory has examined mechanisms whereby chemicals produce mutagenicity in short-term in vitro assays yet fail to produce carcinogenesis in 2-year rodent bioassays. These studies have used mutagenic structural analogs of carcinogenic and noncarcinogenic chemicals for comparison. Our previous studies have determined that differences in the metabolism and disposition of these chemicals were not responsible for their observed carcinogenic differences, but that carcinogenicity correlated with the ability of the respective isomer to induce cell proliferation in the target organ. Mutagenic noncarcinogens such as 2,6-diaminotoluene (DAT), 1-nitropropane (NP), dimethoate, dioxathion, and dichlorvos failed to induce an increase in cell turnover in the target organs. An increase in cell proliferation was observed following exposure to the mutagenic carcinogen analogs 2,4-DAT (liver), 2-NP (liver), and tris(2,3-dibromopropyl)phosphate (kidney). Our recent studies have used transgenic (Big Blue) mice to detect in vivo mutagenesis induced by DAT isomers. Results of these studies demonstrate that administration of the carcinogenic isomer, 2,4-DAT, resulted in an increase in in vivo mutation frequency, whereas administration of the noncarcinogenic isomer, 2,6-DAT, failed to do so. These results indicate that cell proliferation may be requisite for expression of chemical-induced mutagenicity in vivo and thereby accommodate expression of carcinogenicity.

Animals↗

Acute organophosphorus insecticide poisoning in Sri Lanka.

Records of 92 cases of acute organophosphorus (OP) insecticide poisoning were analysed. Of the patients 91% were under 30 years of age and 86% were males. The common agents were Dimethoate, Methamidophos, Malathion, Monocrotophos and Fenthion. Poisoning was due to ingestion with suicidal intent in the majority. In addition to the acute cholinergic features, the other important manifestations were delayed onset respiratory paralysis and delayed polyneuropathy. The overall mortality was 18%.

Adolescent↗

Neurophysiological markers as early signs of organophosphate neurotoxicity.

The central and peripheral nervous system effects of acute and subchronic exposure to three organic phosphoro-acid esters (dimethoate, dichlorvos, parathion-methyl) were studied. CNS-dependent variables included mean EEG amplitude, mean frequency of the EEG, and the activity (power density) of six component frequency bands. Peripheral nervous system evaluations included determinations of conduction velocity, and both relative and absolute refractory periods. Cholinesterase activity was measured in blood, brain and other organs. The results indicate that acute large doses of these agents produce substantial changes in these measures of CNS and PNS function. In subchronic experiments it was found that a six weeks administration of 1/50 LD50 of the chemicals induced early functional changes in both the central and the peripheral nervous systems. It is recommended that when cholinesterase inhibition is detected in humans, functional evaluations of CNS and PNS should follow.

Animals↗

The structure of an enzyme-product complex reveals the critical role of a terminal hydroxide nucleophile in the bacterial phosphotriesterase mechanism.

A detailed understanding of the catalytic mechanism of enzymes is an important step toward improving their activity for use in biotechnology. In this paper, crystal soaking experiments and X-ray crystallography were used to analyse the mechanism of the Agrobacterium radiobacter phosphotriesterase, OpdA, an enzyme capable of detoxifying a broad range of organophosphate pesticides. The structures of OpdA complexed with ethylene glycol and the product of dimethoate hydrolysis, dimethyl thiophosphate, provide new details of the catalytic mechanism. These structures suggest that the attacking nucleophile is a terminally bound hydroxide, consistent with the catalytic mechanism of other binuclear metallophosphoesterases. In addition, a crystal structure with the potential substrate trimethyl phosphate bound non-productively demonstrates the importance of the active site cavity in orienting the substrate into an approximation of the transition state.

Binding Sites↗

Pesticides and PCBs in sediments and fish from the Salton Sea, California, USA.

The Salton Sea, the largest manmade lake in California, is officially designated by the State of California as an agricultural drainage reservoir. The purpose of this study was to determine organochlorine and organophosphorous pesticides, as well as polychlorinated biphenyl (PCB) concentrations in sediments and fish tissues in the Salton Sea and evaluate the relative ecological risk of these compounds. Sediment samples were taken during 2000-2001 and fish tissues (Tilapia mossambique, Cynoscion xanthulu) were collected in May 2001. All samples were analyzed for 12 chlorinated pesticides, 6 organophosphorus pesticides, and 55 polychlorinated biphenyl (PCB) congeners. SigmaDichlorodiphenyltrichloroethane (SigmaDDT) and total PCB concentrations observed in sediments ranged from 10 to 40 and 116 to 304 ng/g dry wt, respectively. DDT/DDD ratios in sediments and fish tissues of the northern Sea in 2001 indicated recent DDT exposure. Lindane, dieldrin, dichlorodiphenylethane (DDE) and total PCB concentrations detected in sediments exceeded probable effect levels established for freshwater ecosystems, and pp-DDE and total PCB concentrations were higher than effect range-median values developed for marine and estuarine sediments. In fish liver, concentrations of endrin and SigmaDDT exceeded threshold effect level established for invertebrates. SigmaDDT concentrations detected in fish tissues were higher than threshold concentrations for the protection of wildlife consumers of aquatic biota. DDE concentrations in fish muscles tissues were above the 50 ng/g concentration threshold for the protection of predatory birds. Dimethoate, diazinon, malathion, chlorpyrifos, disulfoton varied from < or = 0.15 to 9.5 ng/g dry wt in sediments and from < or = 0.1 to 80.3 ng/g wet wt in fish tissues. Disulfoton was found in relatively high concentrations (up to 80.3 ng/g) in all organs from Tilapia and Corvina. These results demonstrate continued contamination of specific organochlorine compounds in sediments and resident fish species of the Salton Sea.

Analysis of Variance↗

Leaching and degradation of 21 pesticides in a full-scale model biobed.

Filling and cleaning of pesticide sprayers presents a potential risk of pollution of soil and water. Three different solutions for handling sprayers have been suggested: Filling and cleaning in the field, filling and cleaning on hard surfaces with collection of the waste water, and filling and cleaning on a biobed, which is an excavation lined with clay and filled with a mixture of chopped straw, sphagnum and soil with turf on top, and with increased sorption capacity and microbial activity for degradation of the pesticides. In the present study the degradation and leaching of 21 pesticides (5 g of each) was followed in an established full-scale model biobed. Percolate was collected and analysed for pesticide residues, and the biobed material was sampled at three different depths and analysed by liquid chromatography double mass spectrometry (LC-MSMS). During the total study period of 563 days, no traces of 10 out of 21 applied pesticides were detected in the percolate (detection limits between 0.02 and 0.9 microg l(-1)) and three pesticides were only detected once and at concentrations below 2 microg l(-1). During the first 198 days before second application, 14% of the applied herbicide bentazone was detected in the leachate with maximum and mean concentrations of 445 and 172 microg l(-1), respectively. About 2% of the initial mecoprop and fluazifop dose was detected in the percolate, with mean concentrations of 23 microg l(-1), while MCPA and dimethoate had mean concentrations of 3.5 and 4.7 microg l(-1), respectively. Leachate concentrations for the remaining pesticides were generally below the detection limit (0.02-0.9 microg l(-1), below 1% of applied). Sorption studies of five pesticides showed that compounds with a low K(d) value appeared in the leachate. After 169 days, all pesticides in the biobed profile were degraded to a level below 50% of the calculated initial dose. Pesticides with K(oc) values above 100 were primarily found in the uppermost 10 cm and degraded slowest due to the low bioavailability. The 11 most degradable pesticides were all degraded such that less than 3% remained in the biobed after 169 days. Following second pesticide application of the biobed, leachate was sampled 215 and 365 days after the treatment. This showed the same pesticides to be leached out and at concentrations comparable to those of the first treatment. The same pesticides as after the first treatment were retained in the biobed.

Chromatography, High Pressure Liquid↗

Fast gas chromatography with solid phase extraction clean-up for ultratrace analysis of pesticide residues in baby food.

A sample preparation method based on single solvent phase extraction and solid-phase extraction (SPE-NH2) clean-up is studied in combination with fast capillary gas chromatography (GC) to determine 18 selected pesticides belonging to various chemical classes in apples, the common raw material for baby food production and baby food, at the concentration level < or = 10 microg/kg maximum residual limit (MRL). Possibilities of mass spectrometry (MS) detector and electron capture detector (ECD) in fast gas chromatography (GC) of samples with complex matrice at ultra trace levels of pesticide residues were studied and compared. MS detection in single ion monitoring (SIM) mode provided higher selectivity compared to ECD. Optimisation of extraction as well as the simplifying of the whole process of sample preparation was carried out. Recoveries obtained at concentration level of 5 microg/kg (the required value for limit of quantification (LOQ) in baby food) were >90%, except of dimethoate (77.7%) and captan (46.4%) with MS detection. The obtained LOQs were at least 1 order lower than 5 microg/kg for the majority of compounds. The repeatability of gas chromatography-mass spectrometry (GC-MS) measurements of the matrix matched standards expressed as relative standard deviation was <11% except of captan and cypermethrin.

Chromatography, Gas↗

Determination of several pesticides in water by solid-phase extraction, liquid chromatography and electrospray tandem mass spectrometry.

The analysis of pesticides in water samples is a problem of primary concern for quality control laboratories due to the toxicity level of these compounds and their public health risk. In order to evaluate the impact of pesticides in the Lisbon drinking water supply system, following the requirements of the European Union Directive 98/83/EC, we developed and validated an analytical method based on the combination of solid-phase extraction with liquid chromatography and tandem mass spectrometry. In this work, several pesticides were studied: imidacloprid, dimethoate, cymoxanil, carbendazime, phosmet, carbofuran, isoproturon, diuron, methidathion, linuron, pyrimethanil, methiocarbe, tebuconazole and chlorpyrifos. Several parameters of the electrospray source were optimized in order to get the best formation conditions of the precursor ion for each pesticide, namely capillary and extractor voltage, cone voltage, cone gas flow rate and desolvation gas flow rate. After optimization of the collision cell energy of the triple quadrupole, two different precursor ion-product ion transitions were selected for each pesticide, one for quantification and one for qualification, and these ions were monitored under time-scheduled multiple reaction monitoring (MRM) conditions. The selection of specific fragment ions for each pesticide guarantees a high degree of selectivity as well as additional sensitivity to quantify trace levels of these pesticides in water samples. This method showed excellent linearity ranges for all pesticides, with correlation coefficients greater than 0.9989. Determination limits (between 0.0041 and 0.0480 microg/L), precision (RSD <9.18%), accuracy and recovery studies in several water samples using solid-phase extraction were also performed.

Chromatography, Liquid↗

A method for genotoxicity detection using random amplified polymorphism DNA with Danio rerio.

The increasing presence of genotoxic pollutants in the aquatic environment has led to the development of quick monitoring methods. We have applied the random amplified polymorphism DNA (RAPD) method to evaluate the toxic effects of genotoxic chemicals. In all 22 normal wide-type Danio rerio (zebrafish), 78 amplified bands were obtained after PCR using the primer set, in which the frequency of emergence above 60% is 21. There do exist four stable bands in the amplified product, which appear in all normal test samples. The zebrafish RAPD fingerprinting database is set up on this base. The RAPD pattern from zebrafish exposed to genotoxic chemicals such as cyclophosphamide in dilution series ranging from 0.1 to 10 mg/L and dimethoate in dilution series ranging from 1.0 to 100 mg/L displayed some changes in polymorphism band patterns including the lost of stable bands. There also exists a distinct distance between the band patterns of exposed zebrafish and the control samples via the cluster method. In addition to that, the result derived from numerical analysis is more sensitive to the result obtained from stable band analysis because it can reveal the distance between the band pattern of the zebrafish exposed to 0.05 mg/L cyclophosphamide and the control sample. These results proved the accuracy and the sensitivity of the two analyses of genotoxicity effect based on RAPD fingerprinting research.

Animals↗

Genotoxicity of the Yamuna River water at Okhla (Delhi), India.

Water samples from the Yamuna River at Okhla (Delhi), India, were concentrated using XAD resins (XAD-4 and XAD-8) and liquid-liquid extraction procedures. Gas chromatographic analysis of liquid-liquid extracted water samples revealed the presence of the pesticides DDT, BHC, dieldrin, endosulfan, aldrin, 2,4-D, dimethoate, methyl parathion, and malathion at concentrations of 14, 25, 2.1, 114, 0.9, 0.6, 0.9, 1.7, and 1.9 ng/L, respectively. The genotoxicity of the extracted water samples was evaluated with the Ames Salmonella/mammalian microsome test, DNA repair-defective mutants, and bacteriophage lambda systems. The results of the Salmonella test demonstrated that the XAD-concentrated water samples had maximum mutagenicity with the TA98 strain both with and without metabolic activation. However, the liquid-liquid-extracted water samples were also found to be mutagenic with one or more of the Ames tester strains, but to a lesser extent as compared with XAD extracts. The damage brought about in the DNA repair-defective mutants in the presence of XAD-concentrated water samples was found to be markedly high as compared with that liquid-liquid-extracted water samples at the dose level of 20 microl/mL culture. All mutants invariably exhibited significant declines in their colony-forming units as compared with their isogenic wild-type counterparts. Survival decreased by 86.3 and 75.5% in the polA- strain after 6 h of treatment with XAD-concentrated and liquid-liquid-extracted water samples, respectively. A significant decrease was also observed in the survival of bacteriophage lambda when treated with the test samples. Mutagenic responses of the liquid-liquid-extracted water samples may not necessarily reflect the mutagenicity of existing pesticides in the test water, because some other organic pollutants might accompany the pesticides in the extract.

Animals↗

Effects of the benzoxazoid DIMBOA, selected degradation products, and structure-related pesticides on soil organisms.

Both lethal and sublethal effects of the benzoxazoid 2,4-dihydroxy-7-methoxy-(2H)-1,4-benzoxazin-3(4H)-one (DIMBOA), the degradation products 6-methoxy-benzoxazolin-2(3H)-one (MBOA), 2-amino-7-methoxy-(3H)-phenoxazin-3-one (AMPO), and 2-acetylamino-7-methoxy-3(H)-phenoxazin-3-one (AAMPO) and the structure-related compounds 2-methoxy-N-(2-oxo-1,3-oxazolidin-3yl)acet-2'=6'-xylidide (oxadixyl), and O,O-diethyl S-[6-chloro-2-oxobenzoxazolin-3-yl)methyl]phosphorodithioate (phosalone) on the collembola Folsomia candida and on the carabid beetle Poecilus cupreus (except phosalone) were determined. Validated laboratory standard methods including reference and control treatments were applied in compliance with prescribed validity criteria. A risk assessment according to the EPPO risk assessment scheme for plant protection products (2003) was carried out. DIMBOA, MBOA, AMPO, AAMPO, and oxadixyl were classified as low-risk compounds for both test organisms. The reference compounds methyl-m-hydroxy-carbanilate-methyl-carbanilate (phenmedipham) and O,O-dimethyl S-[2-(methylamino)-2-oxoethyl]phosphoro-dithioate (dimethoate) were of low and medium risk respectively, to F. candida, but final assessment of the risk to P. cupreus requires further testing. Phosalone was of high risk to F. candida. The results obtained suggest that neither DIMBOA nor the tested degradation products pose a risk to either nontarget soil organism in the field.

Animals↗

Solar photocatalytic degradation of some hazardous water-soluble pesticides at pilot-plant scale.

The technical feasibility and performance of photocatalytic degradation of six water-soluble pesticides (cymoxanil, methomyl, oxamyl, dimethoate, pyrimethanil and telone) have been studied at pilot-plant scale in two well-defined systems which are of special interest because natural solar UV light can be used: heterogeneous photocatalysis with titanium dioxide and homogeneous photocatalysis by photo-Fenton. TiO(2) photocatalysis tests were performed in a 35L solar pilot plant with three Compound Parabolic Collectors (CPCs) under natural illumination and a 75L solar pilot plant with four CPC units was used for homogeneous photocatalysis tests. The initial pesticide concentration studied was 50 mg L(-1) and the catalyst concentrations employed were 200 mg L(-1) of TiO(2) and 20 mg L(-1) of iron. Both toxicity (Vibrio fischeri, Biofix) and biodegradability (Zahn-Wellens test) of the initial pesticide solutions were also measured. Total disappearance of the parent compounds and nearly complete mineralization were attained with all pesticides tested. Treatment time, hydrogen peroxide consumption and release of heteroatoms are discussed.

Aliivibrio fischeri↗

Synergistic effect of entomogenous fungi on some insecticides against Bihar hairy caterpillar Spilarctia obliqua (Lepidoptera: Arctiidae).

A number of fungal parasites infect a wide range of insects and cause epizootics from time to time. Beauveria bassiana (Balsamo) Vuillemin and Metarhizium anisopliae (Metschnikoff) Sorokin are two of the major disease-causing fungi in insects. Investigations were carried out to study the effect of these fungi on the toxicity of endosulfan, imidacloprid, lufenuron, diflubenzuron, dimethoate and oxydemeton methyl against 10-11 days old larvae of Spilarctia obliqua (Walker). For some products the combination treatments showed higher dose mortality response than the sole treatment of fungal conidia or the insecticide. The combination of insecticides with B. bassiana showed 1.26-35.8 fold increase in toxicity of insecticides over sole treatment, while the increase was 1.05-72.0 fold in case of M. anisopliae. Imidacloprid 17.8 SL and oxydemeton methyl 25EC may be used in combination with these fungi for management of S. obliqua.

Animals↗

Acute poisoning with pesticides in the state of Mato Grosso do Sul, Brazil.

Exposure to pesticides has been the source of many acute and chronic health problems in the rural population, mainly in developing countries. The objective of this study was to characterize the poisonings from acute exposure to agricultural pesticides used in the state of Mato Grosso do Sul, Brazil, from 1992 to 2002, which were reported to the Integrated Center of Toxicological Vigilance of the State Health Department. A total of 1355 involuntary (accidental or occupational) and voluntary (intentional self-poisoning) cases were reported during the period of the study. The majority of the poisonings occurred with men ranging in age from 15 to 49 years of age (55.1%). One hundred seventy-six poisonings lead to death, with a case fatality rate (CFR) three times higher than the average Brazilian CFR. The pesticide poisoning rates, per 100,000 inhabitants living in rural areas, ranged from 25 to 65.7 during the period of the study. In 2000, the micro-region of Campo Grande, where the state capital is located, had the highest rate, with 100.5 exposure/100,000 inhabitants, followed by Dourados, the larger agricultural region of the state. Insecticides were involved in 75.7% of the poisoning cases, followed by herbicides, with 12.2% of the cases. The anticholinestherase insecticides methamidophos, carbofuran and monochrotophos were the primary pesticides involved in the poisonings. The insecticide dimethoate was associated with the highest CFR (30.8%). The high rates of pesticide poisoning in the rural populations of certain regions of the state of Mato Grosso do Sul indicate the need for a more detailed study concerning the risk of pesticide poisoning among these populations.

Adolescent↗